Part 1.
TEXAS NATURAL RESOURCE CONSERVATION COMMISSION
Chapter 101.
GENERAL AIR QUALITY RULES
The Texas Natural Resource Conservation Commission (commission) adopts
the
repeal
of §101.29, Emission Credit
Banking and Trading. In addition, the commission adopts
new
§101.300, Definitions; §101.301, Purpose; §101.302,
General Provisions; §101.303, Protocols; §101.304, Program Audits; §101.350,
Definitions; §101.351, Applicability; §101.352, General Provisions; §101.353,
Allocation of Allowances; §101.354, Allowance Deductions; §101.356,
Allowance Banking and Trading; §101.358, Emission Monitoring and Compliance
Demonstration; §101.359, Reporting; §101.360, Level of Activity
Certification; §101.370, Definitions; §101.371, Purpose; §101.372,
General Provisions; §101.373, Protocols; and §101.374, Program Audits.
Adopted
with changes
from the proposed text
as published in the May 25, 2000 issue of the
Texas
Register
(25 TexReg 8137) are new §§101.300, 101.302, 101.303,
101.350 - 101.354, 101.356, 101.358 - 101.360, 101.370, 101.372 - 101.374.
The repeal of §101.29 and new §§101.301, 101.304, and 101.371
are adopted
without changes
and therefore
will not be republished. The repeal and new sections will be submitted to
the United States Environmental Protection Agency (EPA) as a revision to the
Texas state implementation plan (SIP).
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE ADOPTED RULES
The Houston/Galveston (HGA) ozone nonattainment area is classified as Severe-17
under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States
Code (USC), §§7401
et seq.
), and
therefore is required to attain the one-hour ozone standard of 0.12 parts
per million (ppm) by November 15, 2007. In addition, 42 USC, §7502(a)(2),
requires attainment as expeditiously as practicable and 42 USC, §7511a(d),
requires states to submit ozone attainment demonstration SIPs for severe ozone
nonattainment areas such as HGA. The HGA area, defined by Brazoria, Chambers,
Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties has
been working to develop a demonstration of attainment in accordance with 42
USC, §7410. On January 4, 1995, the state submitted the first of its
Post-1996 SIP revisions for HGA.
The January 1995 SIP consisted of urban airshed model (UAM) modeling for
1988 and 1990 base-case episodes, adopted rules to achieve a 9% rate-of-progress
(ROP) reduction in volatile organic compounds (VOC), and a commitment schedule
for the remaining ROP and attainment demonstration elements. At the same time,
but in a separate action, the State of Texas filed for the temporary nitrogen
oxides (NO
x
) waiver allowed by 42 USC, §7511a(f).
The January 1995 SIP and the NO
x
waiver were
based on early base-case episodes which marginally exhibited model performance
in accordance with the United States Environmental Protection Agency (EPA)
modeling performance standards, but which had a limited data set as inputs
to the model. In 1993 and 1994, the commission was engaged in an intensive
data-gathering exercise known as the COAST study. The state believed that
the enhanced emissions inventory, expanded ambient air quality and meteorological
monitoring, and other elements would provide a more robust data set for modeling
and other analysis, which would lead to modeling results that the commission
could use to better understand the nature of the ozone air quality problem
in the HGA area.
Around the same time as the 1995 submittal, the EPA policy regarding SIP
elements and timelines went through changes. Two national programs in particular
resulted in changing deadlines and requirements. The first of these programs
was the Ozone Transport Assessment Group. This group grew out of a March 2,
1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and
Radiation, that allowed states to postpone completion of their attainment
demonstrations until an assessment of the role of transported ozone and precursors
had been completed for the eastern half of the nation, including the eastern
portion of Texas. Texas participated in this study, and it has been concluded
that Texas does not significantly contribute to ozone exceedances in the Northeastern
United States. The other major national initiative that has impacted the SIP
planning process is the revisions to the national ambient air quality standard
(NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing
the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996,
concurrent with the proposal of the standards, the EPA proposed an interim
implementation plan (IIP) that it believed would help areas like HGA transition
from the old to the new standard. In an attempt to avoid a significant delay
in planning activities, Texas began to follow this guidance, and readjusted
its modeling and SIP development timelines accordingly. When the new standard
was published, the EPA decided not to publish the IIP, and instead stated
that, for areas currently exceeding the one-hour ozone standard, that standard
would continue to apply until it is attained. The FCAA requires that HGA attain
the standard by November 15, 2007.
The EPA issued revised draft guidance for areas such as HGA that do not
attain the one-hour ozone standard. The commission adopted on May 6, 1998
and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained
the following elements in response to the EPA's guidance: UAM modeling based
on emissions projected from a 1993 baseline out to the 2007 attainment date;
an estimate of the level of VOC and NO
x
reductions
necessary to achieve the one-hour ozone standard by 2007; a list of control
strategies that the state could implement to attain the one-hour ozone standard;
a schedule for completing the other required elements of the attainment demonstration;
a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the
EPA believed made the previous version of that SIP unapprovable; and evidence
that all measures and regulations required by the FCAA, Title I, Subpart 2
to control ozone and its precursors have been adopted and implemented, or
are on an expeditious schedule to be adopted and implemented.
In November 1998, the SIP revision submitted to the EPA in May 1998 became
complete by operation of law. However, the EPA stated that it could not approve
the SIP until specific control strategies were modeled in the attainment demonstration.
The EPA specified a submittal date of November 15, 1999 for this modeling.
In a letter to the EPA dated January 5, 1999, the state committed to model
two strategies showing attainment.
As the HGA modeling protocol evolved, the state eventually selected and
modeled seven basic modeling scenarios. As part of this process, a group of
HGA stakeholders worked closely with commission staff to identify local control
strategies for the modeling. Some of the scenarios for which the stakeholders
requested evaluation included options such as California-type fuel and vehicle
programs as well as an acceleration simulation mode equivalent motor vehicle
inspection and maintenance program. Other scenarios incorporated the estimated
reductions in emissions that were expected to be achieved throughout the modeling
domain as a result of the implementation of several voluntary and mandatory
state-wide programs adopted or planned independently of the SIP. It should
be made clear that the commission did not propose that any of these strategies
be included in the ultimate control strategy submitted to the EPA in 2000.
The need for and effectiveness of any controls which may be implemented outside
the HGA eight-county area will be evaluated on a county-by-county basis.
The SIP revision was adopted by the commission on October 27, 1999, submitted
to the EPA by November 15, 1999, and contained the following elements: photochemical
modeling of potential specific control strategies for attainment of the one-hour
ozone standard in the HGA area by the attainment date of November 15, 2007;
an analysis of seven specific modeling scenarios reflecting various combinations
of federal, state, and local controls in HGA (additional scenarios H1 and
H2 build upon Scenario Vif); identification of the level of reductions of
VOC and NO
x
necessary to attain the one-hour
ozone standard by 2007; a 2007 mobile source budget for transportation conformity;
identification of specific source categories which, if controlled, could result
in sufficient VOC and/or NO
x
reductions to attain
the standard; a schedule committing to submit by April 2000 an enforceable
commitment to conduct a mid-course review; and a schedule committing to submit
modeling and adopted rules in support of the attainment demonstration by December
2000.
The April 19, 2000 SIP revision for HGA contained the following enforceable
commitments by the state: to quantify the shortfall of NO
x
reductions needed for attainment; to list and quantify potential
control measures to meet the shortfall of NO
x
reductions needed for attainment; to adopt the majority of the necessary rules
for the HGA attainment demonstration by December 31, 2000, and to adopt the
rest of the shortfall rules as expeditiously as practical, but no later than
July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform
a mid-course review by May 1, 2004; and to perform modeling of mobile source
emissions using the EPA mobile source emissions model (MOBILE6), to revise
the on-road mobile source budget as needed, and to submit the revised budget
within 24 months of the model's release. In addition, if a conformity analysis
is to be performed between 12 months and 24 months after the MOBILE6 release,
the state will revise the motor vehicle emissions budget (MVEB) so that the
conformity analysis and the SIP MVEB are calculated on the same basis.
In order for the state to have an approvable attainment demonstration,
the EPA has indicated that the state must adopt those strategies modeled in
the November 1999 submittal and then adopt sufficient controls to close the
remaining gap in NO
x
emissions. The modeling
and other analysis supporting these rules and the HGA SIP indicate a gap of
an additional 88.8 tons per day (tpd) of NO
x
reductions is necessary for an approvable attainment demonstration. The predicted
emission reductions from these rules are necessary to successfully demonstrate
attainment.
The emission reduction requirements included as part of this SIP revision
represent substantial, intensive efforts on the part of stakeholder coalitions
in the HGA area. These coalitions, involving local governmental entities,
elected officials, environmental groups, industry, consultants, and the public,
as well as the commission and the EPA, have worked diligently to identify
and quantify potential control strategy measures for the HGA attainment demonstration.
Local officials from the HGA area have formally submitted a resolution to
the commission, requesting the inclusion of many specific emission reduction
strategies.
This rule adoption is one element of the control strategy for the HGA SIP.
Adoption and implementation of this control strategy is necessary in order
for the HGA nonattainment area to comply with the requirements of the FCAA
and achieve attainment for ozone. Additional elements of the control strategy
for the HGA SIP are being adopted concurrently in this issue of the
The amount of NO
x
reductions required for
the area to attain the ozone NAAQS has been estimated by extensive use of
sophisticated air quality grid modeling, which because of its scientific and
statutory grounding, is the chief policy tool for designing emission reduction
strategies. The FCAA, 42 USC, §7511a(c)(2), requires the use of photochemical
grid modeling for ozone nonattainment areas designated serious, severe, or
extreme. The modeling has been conducted with input from a technical oversight
committee. Commission staff have continued to improve the air quality modeling
technology and refine emission inventory data. Numerous emission control strategies
were considered in developing the modeling. Varying degrees of reductions
from point sources, on-road and non-road mobile sources, and area sources
were analyzed in multiple iterations of modeling, to test the effectiveness
of different NO
x
reductions. The attainment demonstration
modeling and other analysis submitted for public hearing and comment concurrently
with the HGA SIP show that a significant amount of NO
x
reductions practicably achievable are necessary from ozone control
strategies in order for the HGA nonattainment area to achieve the ozone NAAQS
by 2007, including reductions from surrounding counties included in the HGA
consolidated metropolitan statistical area (CMSA).
Additionally, reductions associated from the ozone control strategies that
will be implemented outside the HGA nonattainment area will benefit the HGA
nonattainment area. This is due to the regional nature of air pollution, the
contribution from mobile sources, and the economies of scale and associated
market advantages related to distribution networks for some strategies. At
the time the 1990 FCAA Amendments were enacted, the focus on controlling ozone
pollution was centered on local controls. However, for many years an ever
increasing number of air quality professionals have concluded that ozone is
a regional problem requiring regional strategies in addition to local control
programs. As nonattainment areas across the United States prepared attainment
demonstration SIPs in response to the 1990 FCAA Amendments, several areas
found that modeling attainment was made much more difficult, if not impossible,
due to high ozone and ozone precursor levels entering from the boundaries
of their respective modeling domains, commonly called transport. Recent science
indicates that regional approaches may provide improved control of ozone air
pollution.
The current SIP revision contains rules, enforceable commitments, photochemical
modeling analyses, and calculation of the remaining NO
x
reductions required to reach attainment (gap calculation) in support
of the HGA ozone attainment demonstration. In addition, this SIP contains
post-1999 ROP plans for the milestone years 2002 and 2005, and for the attainment
year 2007. The SIP also contains enforceable commitments to implement further
measures, if needed, in support of the HGA attainment demonstration, as well
as a commitment to perform and submit a mid-course review.
The HGA ozone nonattainment area will need to ultimately reduce NO
The emissions banking and trading program has been designed to offer flexibility
in generating and using emission reduction credits (ERCs), mobile emission
reduction credits (MERCs), discrete emission reduction credits (DERCs), and
mobile discrete emission reduction credits (MDERCs). Flexibility has been
built into the rules to create incentives for the early or permanent retirement
of VOC and NO
x
emissions. The intent of the rules
is to also streamline the emissions banking and trading program by combining
the stationary credits with mobile credits to achieve continuity within the
banking programs.
New §§101.300 - 101.304 are grouped into Subchapter H, Division
1, Emission Credit Banking and Trading. The rules consolidate the requirements
for generating, using, banking, and trading ERCs and MERCs. The revisions
to the rules are intended to achieve consistency between the rules governing
the use of ERCs/MERCs and DERCs and MDERCs. The revisions to the rules also
address concerns raised by the EPA regarding current rules on how reductions
are calculated as surplus and to ensure that emission reductions are not double-counted,
that is, not banked as credits and relied upon as SIP reductions. These sections
would reduce the life of ERCs/MERCs after January 2, 2001 to five years to
restrict the use of ERCs/MERCs to meet current environmental conditions. The
rules require the registration of emission reductions as ERCs/MERCs within
180 days of the actual reduction and add recordkeeping requirements to sources
generating or using ERCs/MERCs.
New §§101.350 - 101.354, 101.356, and 101.358 - 101.360 are grouped
into Subchapter H, Division 3, Mass Emissions Cap and Trade Program. These
sections implement a mandatory annual NO
x
emission
cap on all existing stationary facilities located in the HGA area that emit
ten tons or more per year (tpy) of NO
x
and that
have SIP emission requirements in 30 TAC §117.106, Emission Specifications
for Attainment Demonstrations, §117.206, Emission Specifications for
Attainment Demonstrations, and §117.475, Emission Specifications. The
cap would be enforced by the allocation, trading, and banking of allowances.
An allowance is the equivalent of one ton of NO
x
emissions. NO
x
is a precursor gas that reacts
with VOCs in the presence of sunlight to form ground-level ozone. This NO
At this time, the commission will cap only those sources located in the
eight-county HGA area. The commission will continue to evaluate ozone control
strategies and may extend the cap and trade program to include other regions
of the state in future rulemaking.
New §§101.370 - 101.374 are grouped into Subchapter H, Division
4, Discrete Emission Credit Banking and Trading. The rules consolidate the
requirements for generating, using, banking, and trading DERCs and MDERCs.
The revisions to the rules are intended to achieve consistency between the
rules governing the use of ERCs/MERCs and DERCs/MDERCs. The revisions to the
rules also address concerns raised by the EPA regarding current rules on how
reductions are calculated as surplus and to ensure that emission reductions
are not double-counted, that is, not banked as credits and relied upon as
SIP reductions.
SECTION BY SECTION DISCUSSION
DIVISION 1
New §101.300 contains the definitions to be used within Subchapter
H, Emissions Credit Banking and Trading, Division 1, Emission Credit Banking
and Trading. The definitions of "Activity," "Actual emissions," "Area Source,"
"Certified," "Emission Reduction Credit (ERC)," "Emission Reduction Strategy,"
"Generator," "Permanent," "Quantifiable," and "Shutdown" were defined in §101.29
and are transferred unchanged to §101.300.
The following definitions have been moved from §101.29 to §101.300
and amended. "Applicable emission point" is revised to refer to the emission
point generating an emission reduction or using an emission credit. This revision
will allow for consistency with the use of terms throughout the adopted rule
language. The definition of "Baseline" is amended to limit the emissions occurring
prior to a reduction strategy to levels not to exceed the most recent level
of emissions reported in the emission inventory used for SIP determinations.
The definition of "Baseline activity" is amended to describe a source's actual
level of activity based on actual data averaged over any consecutive two calendar
year periods during the most recent year of emissions inventory used for SIP
determinations or subsequent year(s). For sources in existence less than 24
months or not having two complete calendar years of data, a shorter time period,
not less than 12 months, may be considered by the executive director. The
definition of "Baseline emission rate" is amended to refer to the source's
rate of emissions per unit of activity during the baseline activity period.
The definition of "Curtailment" is amended to mean a reduction in activity
level at any stationary or mobile source. The definition of "Mobile emission
reduction credit (MERC or mobile credit)" is amended to be a credit representing
the amount of emission reductions from a mobile source strategy. These emission
reductions are voluntary and must be in addition to compliance with requirements
of state and federal regulations. MERCs are any enforceable, permanent, and
quantifiable emission reduction (exhaust and/or evaporative) generated by
a mobile source, which has been banked in accordance with the rules of the
commission. MERCs can be banked, purchased, traded, and sold to meet clean
air mandates for specified air programs and MERCS may be applied to the emission
reduction obligations of another air quality source or to air quality attainment
goals. The definition was revised to clarify that MERCs are expressed in terms
of tons per year. "Most stringent allowable emissions level" is amended to
include a reference to state emission limits. The definition of "Ozone season"
is revised to be the portion of the year when ozone monitoring is required
to occur in a specific geographic area. This amendment removes specific references
to dates for a given nonattainment area. "Protocol" is amended to refer to
replicable and workable methods for mobile, stationary, or area sources. "Real
reduction" means a reduction in actual emissions as opposed to a reduction
in allowable emissions. "Surplus" is amended to refer to an emission reduction
which is not otherwise required of a source by any state or federal law, regulation,
or agreed order and is beyond the emissions level utilized for SIP determinations.
"User" is amended to refer to the owner or operator which acquires and uses
emission credits to meet a regulatory requirement, demonstrate compliance,
or offset an emission increase.
The following new definitions are added to §101.300. "Baseline emissions"
is defined as the source's total actual emissions based on the baseline activity
and emission rate. An "Emission credit" is defined as a credible emission
reduction such as an "Emission reduction credit" or "Mobile emission reduction
credit." A new definition of "Emission reduction" is added as an actual reduction
of emissions from a stationary or mobile source. "Mobile emission baseline"
is defined as a mobile source reduction that occurs prior to a mobile emission
reduction strategy, considering all limitations required by applicable state
and federal regulations. A valid mobile emission baseline could be calculated
by either use of measured emissions of an appropriately sized sample of the
participating mobile sources using an approved EPA test procedure or by using
estimated emissions of the participating mobile sources using the most recent
edition of the EPA's mobile emissions factor model or other applicable model.
The baseline cannot be higher than the emissions that are estimated in the
SIP for that vehicle. "Mobile source" is defined as on-road (highway) vehicles
(e.g., automobiles, trucks, and motorcycles) and non-road vehicles (e.g.,
trains, airplanes, agricultural equipments, industrial equipment, construction
vehicles, off-road motorcycles, and marine vessels). A "Mobile source baseline
activity" is defined as the mobile source's level of activity during the applicable
mobile source baseline year. "Mobile source baseline emissions" is defined
as the mobile source's total emissions based on the product of mobile source
baseline activity and mobile source baseline emission rate. "Source" is a
point of origin of air contaminants, whether privately or publicly owned or
operated. Upon request of a source owner, the executive director shall determine
whether multiple processes emitting air contaminants from a single point of
emission will be treated as a single source or as multiple sources.
New §101.301 states that the purpose of Division 1 is to allow an
operator of a source to generate and use emission credits. The wording of
this section has been revised from the previous language in §101.29 to
refer to both ERCs and MERCs as emission credits, unless the rule language
specifically refers to only one of these emission credits. This new section
also states that participation in the program is voluntary.
New §101.302 contains the general provisions for the Emission Credit
and Trading Program (Division 1). The wording of this section has been revised
from the previous language in §101.29 to refer to both ERCs and MERCs
as emission credits, unless the rule language refers to only one of these
emission credits. Language was added to clarify that the EPA must also grant
approval before a reduction of one pollutant may be used to meet the requirements
of another pollutant. The certification requirements of an emission credit
have been revised to only allow credits which have occurred after the most
recent year of emissions inventory used for SIP determinations and to require
the source's annual emissions to have been represented in the emissions inventory
of the most recent year of emissions inventory used for SIP determinations
prior to the submittal of the emission credit application. Rule language has
been added to this division which would not allow emission credits which are
certified as ERCs or MERCs to be recertified as emission credits under any
other division within Subchapter H. The rules associated with eligible sources
have been changed to be consistent with the previous language of §101.29
for discrete emission credits. The changes allow for stationary sources (including
area sources), mobile sources, and stationary sources (including area sources)
or mobile sources associated with agencies under §101.30 to be eligible
to generate emission credits. Effective January 2, 2001, the life of an emission
credit would be revised to be available for use for 60 months from the date
of the reduction except to the extent regulatory changes reduce or invalidate
the reduction. ERCs, for which an administratively complete application has
been received prior to January 2, 2001, would continue to be available for
120 months from the date of the reduction except to the extent regulatory
changes reduce or invalidate the reduction. The geographic scope would remain
the same as previously stated in §101.29, except the new rule language
allows for the trading of emission credits achieved in the county, state,
or nation provided the applicant can demonstrate an improvement to the air
quality in the county of use and the demonstration is approved by the executive
director and the EPA. To be consistent with the previous language of §101.29,
rule language is added which allows for the possibility of the trading of
emission credits to be discontinued by the executive director, with commission
approval, as a remedy for problems caused by localized trading of emission
credits. The rules regarding the registry were revised from the proposal to
state that a unique number is assigned to certificates and not to individual
tons of ERCs or MERCs. Recordkeeping requirements have been revised to require
users to maintain a copy of all notices and information submitted to the registry
for at least two years after the beginning of the use period along with the
name, emission point number (EPN), and facility identification number (FIN)
of each unit using emission credits, the amount of emission credits being
used, and the specific identification number of the emission credits being
used. The rule language concerning public information has been changed to
be consistent with the discrete emission reduction requirements language previously
located in §101.29(d)(1)(L). All information submitted with a notice
or report regarding the nature and quantity of emissions associated with the
use or generation of an emission credit is public information and will not
be considered confidential. All non-confidential notices and information regarding
generation, use, and availability of emission credits may be obtained from
the Office of Permitting, Remediation, and Registration (OPRR). In addition,
rule language is adopted which allows the executive director to prohibit a
company from participating in the program if the company has violated or abused
the program.
New §101.303 outlines the required protocols of generating, calculating,
certifying and registering, using, and transferring emission credits. This
section requires emission credits to be determined based on established EPA
protocols when available, actual monitoring results, or calculated using good
engineering practices. The procedures previously in §101.29 regarding
the various means for generating emission credits are transferred unchanged
to this section. The rule addresses procedures for calculating MERCs although
most mobile source strategies will likely only qualify for MDERCs. MERCs would
be available for mobile source strategies that are ongoing, creating the same
amount of mobile reduction each year. Language is added which prohibits the
generation of credits if the emissions have been transferred to another unit.
This additional language eliminates the potential for a company to shut down
a unit to generate emission credits, and then alter the operation of another
piece of equipment to take the place of the shut down unit which would increase
the emissions at the altered unit. The new rules require companies to apply
for emission credits within 180 days of generation, except that those sources
that have implemented strategies prior to the effective date of this rule
will be given until June 1, 2001 to apply. New language has been added to
the rules specifying the information which must be submitted. The information,
which is to be submitted on the EC-1 Form, includes the information necessary
for the executive director to review the application in accordance with the
adopted rules and to properly administer the program. Language was added to
clarify that the most stringent emission rate would be determined by also
reviewing local, state, and federal statutory requirements. Applicants will
be notified in writing if the executive director denies the application. The
new rule language specifically states the commission's accepted practice that
emissions credits will be determined and certified to the nearest tenth of
a ton per year. As was previously stated in §101.29, the new section
states that emission credits are determined and certified by using the EPA
methodologies, monitoring results, or otherwise good engineering practices,
and all emission credits are deposited in the registry and reported as available
credits until they are used, withdrawn, or expired. As was previously contained
in §101.29, the new section would list the mechanisms which can be used
to make emission credits enforceable. Rule language has been added which lists
the OPCRE-1 Form as an enforceable mechanism to establish new emission limits
for grandfathered sources when applying for emission credits. Rule language
has also been added to make MERCs enforceable by registering them on a form
approved by the executive director or by an agreed order that will set new
maximum allowable mobile source emission limits which are not required to
be implemented by a rule. The language would limit the use of emission credits
if there are permits under the same account number which contain a condition
or conditions which preclude such use. As was previously allowed in §101.29,
the new section allows ERCs to be used for offsets, mitigation offsets, and
alternative compliance with reasonably available control technology (RACT)
or SIP requirements. As has been the commission's practice, the language allows
the use of emission credits for netting only by the original applicant if
the emission credits have not been previously sold or otherwise used and also
allows the use of emission credits for other provisions within the guidelines
of local, state, and federal laws. The section allows MERCs to be used as
offsets, mitigation offsets, alternative compliance with RACT or SIP requirements,
compliance with fleet requirements as allowed by the Texas Clean Fleet Program
Requirements for Motor Vehicle Fleets, or other provisions as allowed within
the guidelines of local, state, and federal laws. The requirements for compliance
with §117.570, Use of Emissions Credits for Compliance, except for the
equations for determining 30-day rolling average emission limits, are changed
to allow for emission reduction calculations in accordance with the methodology
of this new division. These revisions replace the former equations previously
located in §117.570. The equations for calculating 30-day rolling average
emission limits have been relocated from §117.570 to this section. The
procedure for notifying the commission of the intent to use emission credits
in accordance with 30 TAC Chapter 114, Control of Air Pollution from Motor
Vehicles, §115.950, Emissions Trading, and §117.570 and any other
commission rules is revised to require the submittal of the EC-3 Form. The
timelines for the review of this submittal have been removed from the rule
language, revised, and included in the Emission Banking and Trading Program
Technical Guidance Package. As previously required in §101.29, an additional
10% of emission credits will be retired as an environmental contribution.
The section states that the user of credits shall submit an EC-3 Form along
with the emission credit certificates when using the credits as offsets in
accordance with 30 TAC Chapter 116, Division 7, Emission Reductions: Offsets,
or for alternative compliance with 30 TAC Chapters 114, 115, or 117. The procedure
for transfer is revised to require emission credit certificate owners to submit
an EC-4 Form, including the sale price, to the agency prior to the transfer.
Transfers would only be considered final after the executive director has
completed the transaction. This is a change to the previous language in §101.29,
which requires notification within 30 days of the transfer. As previously
stated in §101.29, the new section states that the emission credits may
be withdrawn from the registry at any time prior to the expiration date of
the credit, and that emission reductions which have been certified as credits
and have expired may still be used by the original owner for netting in accordance
with §116.150. The section requires applicants needing offsets for a
new source review permit to identify the credits at the time of permit issuance
and to provide the original emission credit certificate prior to operation.
It should be noted that emission credits will be evaluated to ensure that
they are surplus at the time of use. The section requires that any other uses
of credits be approved by the executive director prior to commencement of
the intended use. Rule language added allows an applicant to file a motion
for reconsideration with the executive director within 60 days of denial of
use of emission credits.
New §101.304 requires the executive director to perform an audit of
the emission reduction program within three years of the effective date of
the new division and every three years thereafter. The audit would evaluate
the timing of credit generation and use, the impact of the program on the
SIP, availability and cost of credits, compliance by participants, and any
other elements chosen by the executive director.
DIVISION 3
New §101.350 contains the definitions to be used with Subchapter H,
Emissions Credit Banking and Trading, Division 3, Mass Emission Cap and Trade
Program. In response to comments received, the definition of "Allowance" has
been modified from the proposal and is now defined as the authorization to
emit one ton of NO
x
during a control period as
expressed in tenths of a ton. The definition of "Authorized account representative"
is the person authorized, in writing, to transfer and otherwise manage allowances.
The definition of "Banked allowance" is an allowance which is not used to
reconcile emissions in the designated year of allocation, but which is carried
forward for up to one-year and noted in the compliance or broker account as
banked. The definition of "Broker" is a person not required to participate
in the requirements of this division who opens an account under this division
for the purpose of banking and trading allowances. The definition of "Broker
account" is the account where allowances held by a broker are recorded. Allowances
held in a broker account may not be used to satisfy compliance requirements
for this division. The definition of "Compliance account" is the account where
allowances held by a facility or multiple facilities at a single site are
recorded for the purposes of meeting the requirements of this division. This
definition was modified from the proposal to clearly identify the intent when
referring to a piece of equipment that is emitting NO
x
. It was necessary to add language concerning a single site to clarify
the correspondence of a single compliance account to a single site. The reference
to sources not under common ownership or control was deleted as it was unnecessary
and ambiguous. Separate sites with facilities subject to the cap and trade
program will automatically be assigned separate compliance accounts unless
a single property designation is obtained. The definition of "Control period"
is the 12-month period beginning January 1 and ending December 31 of each
year. The initial control period would begin January 1, 2002. The definition
of "Level of activity" is the amount of activity at a source measured in terms
of production, fuel use, raw materials input, or other similar units that
have a direct correlation with the economic output and emission rate of the
source (i.e., mass emitted per unit of activity). The definition of "Person"includes,
for the purpose of issuance of allowances under this division, an individual,
a partnership of two or more persons having a joint or common interest, a
mutual or cooperative association, and a corporation. The new section refers
to the following existing definitions: "Houston/Galveston (HGA) ozone nonattainment
area" as defined in §101.1; and "Site" as defined in §122.10, General
Definitions. The definition of "Site" was added since publication of the proposal.
The definition of "Source" was deleted from the adoption because the use of
the term "facility" is more appropriate when describing pieces of equipment
emitting NO
x
.
New §101.351 states that the requirements of Division 3 apply to all
stationary facilities which emit NO
x
in the HGA
nonattainment area subject to the emission specifications under §§117.106,
117.206, and 117.475 and that have a design capacity to emit ten tons or more
per year of NO
x
. The term facility has been substituted
for source to identify specific equipment emitting NO
x
. The commission intends to propose a revision to this section to
clarify that the cap and trade rules apply to all facilities subject to Chapter
117 at sites where these facilities collectively have a design capacity to
emit ten tons or more per year of NO
x
. This clarification
reflects the original intent of the commission and the commission will propose
this revision to allow for notice and comment on the clarification shortly
after adoption of these rules.
New §101.352 states that allowances may only be used as described
in Division 3 and cannot be used to meet or exceed the limitations of any
annual emission limitation authorized under Chapter 116, Subchapter B, any
applicable rule or law, or for netting purposes to avoid the applicability
of federal and state new source review (NSR) requirements. The new section
requires that each site shall hold a quantity of allowances in its compliance
account on February 1 equal to or greater than the total emissions of NO
New §101.353 describes how allowances will be allocated to individual
facilities. This section has been revised since proposal for the adoption
for clarity, to change the reduction schedule, and to revise the amount of
necessary reductions. Initially, for any facility operating prior to January
1, 1997, allowances will be based on its actual level of activity from 1997,
1998, and 1999 multiplied by the higher of the facility's actual emission
factors from 1997, 1998, and 1999 (not to exceed any applicable federal or
state regulation, rule, or permit limit) or the facility's emission factor
listed in Chapter 117. For a facility not operating prior to January 1, 1997
and which has submitted, under Chapter 116, Control of Air Pollution by Permits
for New Construction or Modification, an application which the executive director
has determined to be administratively complete before January 2, 2001 or has
qualified for a permit by rule under Chapter 106, Permits by Rule, and has
commenced construction before January 2, 2001, allowances will be equal to
the facility's level of activity as authorized by the executive director,
(until such time that two complete consecutive calendar years of actual level
of activity data is available), multiplied by the higher of the facility's
authorized emission factor (until such time an emission factor averaged over
the most recent two consecutive calendar years is available, not to exceed
any applicable federal or state regulation, rule, or permit limit) or the
facility's emission factor listed in Chapter 117. For a facility using alternative
emission specifications as allowed in §§117.106(c)(2), 117.206(c)(17),
or 117.475(c)(3) beginning allowances will be calculated using the lowest
level of activity as determined by the facility's 1997 through 1999 level
of activity average, two complete calendar years of average level of activity
subsequent to 1997, or a level of activity limited by an enforceable limit
or commitment multiplied by the higher of the facility's authorized emission
factor (until such time an emission factor averaged over the most recent two
consecutive calendar years is available, not to exceed any applicable federal
or state regulation, rule, or permit limit) or the facility's emission factor
listed in Chapter 117. The purpose for using a two- or three-year average,
when available, is to limit the effect of a year in which the activity level
was uncharacteristically low or high for a facility. The purpose for using
the higher of the facility's actual or allowable emission factor or its emission
factor as listed in Chapter 117 is to prevent penalizing those facilities
already emitting or authorized to emit at levels equal to or lower than the
requirements in Chapter 117.
For all boilers, auxiliary steam boilers, and stationary gas turbines within
an electric power generating system as defined in §117.10, Definitions,
allowances will be reduced by 47% of the required reductions in Chapter 117
beginning January 1, 2003. Beginning April 1, 2004, allowances for boilers,
auxiliary steam boilers, and stationary gas turbines will be reduced by 95%
of the required reduction. Beginning April 1, 2007 and for all subsequent
control periods allowances for boilers, auxiliary steam boilers, and stationary
gas turbines will be reduced by 100% of the required reductions.
For all other sources, allowances will be reduced by 44% of the required
reductions in Chapter 117 beginning January 1, 2004. Beginning April 1, 2005,
allowances for boilers, auxiliary steam boilers, and stationary gas turbines
will be reduced by 89% of the required reduction. Beginning April 1, 2007
and for all subsequent control periods allowances will be reduced by 100%
of the required reductions. The commission believes that this revised compliance
schedule facilitates a determination at the mid-course review by May 1, 2004
to ensure that the final 5% of the reductions from boilers, auxiliary steam
boilers, and stationary gas turbines within an electric power generating system,
as defined in §117.10, and the final 11% of the reductions from other
sources are necessary or sufficient for attainment of the ozone standard.
The section states that any new or modified facility will not be allocated
any allowances if that facility has submitted, under Chapter 116, Control
of Air Pollution by Permits for New Construction or Modification, an application
which the executive director has determined to be administratively complete
on or after January 2, 2001 or has qualified for a permit by rule under Chapter
106, Permits by Rule, and has commenced construction on or after January 2,
2001. These new or modified facilities will be required to obtain allowances
an on annual basis from other facilities already participating in the cap
and trade program or by obtaining DERCs or MDERCs. This requirement applies
only to those facilities identified in §101.351 relating to applicability.
The section states that if a facility emits more NO
x
than was held in the compliance account on January 31 following the
control period, allowances for the next control period will be reduced by
the amount equal to the emission exceeding the compliance account plus an
additional 10%. Based on comments received, language was added from the proposal
to clarify that this section does not preclude additional enforcement action
by the executive director. The section states that allowances would be allocated
by January 1 of each control period, beginning in 2002, that the annual allocation
of allowances may be adjusted by the executive director for any new or existing
SIP requirement, and that allowances may be added or subtracted from compliance
accounts after reviewing the reports required in §101.359. The section
allows the executive director to deviate from the allocation methodology in
extenuating circumstances. The commission added language stating that owners
or operators of facilities seeking deviations from the allocation methodology
of this section due to extenuating circumstances must apply to the executive
director no later than June 1, 2001. Based on comments received, the commission
added language stating that allowances allocated based on historical activity
levels will continue to be allocated despite subsequent shutdowns or reductions
in activity levels.
New §101.354 describes how allowances will be subtracted out of compliance
accounts. The section states that allowances are deducted from a site's compliance
account in tenths of tons based on the facility's level of activity during
a control period and multiplied by the facility's emission factor during the
control period. This change from the proposal, which used whole tons, was
based on comments. The commission added language which states that another
method to determine the number of allowances to be deducted from a compliance
account can be used in lieu of the method mentioned above as determined by
the executive director. This was added for cases where continuous monitoring
data, stack sampling, or other methods might provide better results when determining
a facility's actual emissions. The commission added language which requires
the executive director to deduct the most recently allocated allowances before
deducting banked allowances. This language was added to minimize the possible
effect on the emission cap by the accumulation of allowances. The commission
added language that states that allowances allocated based on authorized levels
of activity and not on historical levels of activity may only be used by the
facility for which they were allocated and may not be used by other facilities
at the same site during the same control period. Allowances allocated based
on authorized levels of activity are intended to allow new and modified facilities
an authorization to emit until such time as two complete consecutive calendar
years of data is available. These allowances are not intended to provide additional
flexibility to existing facilities at the site. The section states that a
facility shall hold a quantity of allowances equal to or greater than its
actual NO
x
emissions by February 1 for the preceding
control period.
The new §101.356 describes how allowances may be traded and banked.
Allowances may generally be banked for future use or traded during the control
period for which they are allocated or the following control period. Any allowance
not used for compliance may be banked or traded for use in the following control
period, with the exception of unused allowances allocated in variables (2)(B)
and (3)(B) in Figure 30 TAC §101.353(a). The section states that allowances
that aren't expired or used could be traded at any time after they have been
allocated, again with the exception of allowances allocated in variables (2)(B)
and (3)(B) in Figure 30 TAC §101.353(a). Only authorized account representatives
may trade allowances. Trade requests would be made through the submittal of
a completed ECT-2 Form. As part of the application, the account representative
shall report the price paid per allowance and shall submit the ECT-2 Form
within 15 days prior to be deposited into the transferee's broker or compliance
account. Trades would be completed through the executive director and would
be considered complete when the executive director issues a letter finalizing
the trade. This section would allow for the use of discrete emission credits
in accordance with Chapter 101, Subchapter H, Division 4 in place of allowances
for compliance with Division 3. This section has been revised based on comments
to clarify how DERCs and MDERCs may be used. The section has been revised
to state that MDERCs may be used in lieu of allowances on a one-to-one ratio.
DERCs generated prior to January 1, 2005 may be used in lieu of allowances
at a one-to-one ratio prior to January 1, 2005. DERCs generated prior to January
1, 2005 may be used in lieu of allowances at a ten-to-one ratio after January
1, 2005. DERCs generated on or after January 1, 2005 may be used in lieu of
allowances at a one-to-one ratio on or after January 1, 2005. In addition,
no more than 10,000 DERCs will be allowed to be used in the entire HGA nonattainment
area per year on or after January 1, 2005. The executive director will develop
guidance to determine how the 10,000 DERCs will be distributed among all applicants
requesting their use. Language was added to clarify that the 10% environmental
contribution and the 5% compliance margin of Division 4 do not apply to the
use of DERCs and MDERCs in lieu of allowances. The commission has also reduced
the 45 day requirement to submit a notice of intent to use to 30 days. In
response to comments the commission is evaluating the use of ERCs in lieu
of allowances and may consider future rulemaking. The section was also revised,
based on comments, to require an audit of the cap and trade program every
three years. The audit will evaluate the program, its success and failures,
its impact on the SIP, and any other pertinent information.
New §101.358 states that if monitoring is required of a facility under
a federal or state program, that monitoring or other data shall be used to
determine actual NO
x
emissions. Facilities not
required to monitor shall calculate actual NO
x
emissions using generally accepted engineering practices, including calculation
methodologies in general use and accepted in NSR permitting.
New §101.359 states that facilities shall submit by March 31 a completed
ECT-1 Form detailing the amount of actual NO
x
emission for the preceding control period and shall include the methods used
in determining the NO
x
emissions and a summary
of all final trades.
New §101.360 states that all facilities required to participate in
the cap and trade program would be required to submit a completed ECT-3 Form
certifying their historical level of activity by June 30, 2001. This section
was revised to clarify that the level of activity must be submitted not only
for facilities with three complete years of historical data from 1997 through
1999, but also for the other facilities that will receive allowances based
on their authorized activity levels and subsequently, their two years of actual
data. This information will be used to calculate each facility's allocations.
DIVISION 4
New §101.370 contains the definitions to be used within Subchapter
H, Emissions Credit Banking and Trading, Division 4, Discrete Emission Credit
Banking and Trading. The definitions of "Activity," "Actual emissions," "Area
Source," "Certified," "Emission Reduction Strategy," "Generator," "Permanent,"
"Quantifiable," "Shutdown," and "Use period" were defined in §101.29
and were transferred unchanged to §101.370.
The following definitions were moved from §101.29 to §101.370
and amended. "Applicable emission point" is revised to refer to the emission
point generating an emission reduction or using an emission credit. This revision
allows for consistency with the use of terms throughout the rule language.
The definition of "Baseline" is amended to limit the emissions occurring prior
to a reduction strategy to levels not to exceed the most recent level of emissions
reported in the emission inventory used for SIP determinations. The definition
of "Baseline activity" is amended to describe a source's actual level of activity
based on actual data averaged over any consecutive two calendar year period
during the most recent year of emissions inventory used for SIP determinations
or subsequent year(s). For sources in existence less than 24 months or not
having two complete calendar years of data, a shorter time period, not less
than 12 months, may be considered by the executive director. The definition
of "Baseline emission rate" is amended to refer to the source's rate of emissions
per unit of activity during the baseline activity period. The definition of
"Curtailment" is amended to mean a reduction in activity level at any stationary
or mobile source. The definition of "Discrete emission reduction credit" is
revised to be a credible emission reduction that is created during a generation
period, quantified after the period in which emission reductions are made,
and expressed in tons. This change provides consistency with the new terms
and definitions of the adopted rules. The definition of "Ozone season" is
revised to the portion of the year when ozone monitoring is federally required
to occur in a specific geographic area. "Protocol" is amended to refer to
replicable and workable methods for mobile and stationary sources. The definition
of "Real reduction" means a reduction in actual emissions as opposed to a
reduction in allowable emissions. "Surplus" is amended to refer to an emission
reduction which is not otherwise required of a source by any state or federal
law, regulation, or agreed order and is beyond the emissions level utilized
for SIP determinations. "User" is amended to refer to the owner or operator
which acquires and uses emission credits to meet a regulatory requirement,
demonstrate compliance, or offset an emission increase. "Use strategy" is
revised to refer to the use of "emission credits" which is more consistent
with the terms in the new rules.
The following new definitions are added to §101.370. "Baseline emissions"
is defined as the source's total actual emissions based on the baseline activity
and baseline emission rate. A "Discrete emission credit" is defined as a credible
emission reduction such as a "Discrete emission reduction credit" or "Mobile
discrete emission reduction credit." A definition of "Emission reduction"
is added as an actual reduction of emissions from a stationary or mobile area
source. The "Generation period" is defined as the discrete period of time,
not exceeding 12 months, over which a discrete emission reduction credit is
created. The definition of "Level of Activity" was added in response to comments.
The definition states that the level of activity is the amount of activity
at a source measured in terms of production, fuel use, raw material input,
or other similar units that have a direct correlation with the economic output
and emission rate of the source (i.e., mass emitted per unit of activity).
A "Mobile discrete emission reduction credit (MDERC or discrete mobile credit)"
is defined as a credit that is surplus, generated by a mobile source strategy.
It is a creditable emission reduction that is created during a generation
period, quantified after the period in which emissions reductions are made,
and expressed in tons. "Mobile emissions baseline" is defined as mobile emissions
which occur prior to a mobile emission reduction strategy, considering all
limitations required by applicable state and federal regulations. A valid
mobile emission baseline could be calculated by either using measured emissions
of an appropriately-sized sample of the participating mobile sources using
an approved EPA test procedure or by using estimated emissions of the participating
mobile sources using the most recent edition of the EPA's mobile emissions
factor model or other applicable model. The baseline cannot be higher than
the emissions which are estimated in the SIP for that vehicle. "Mobile source
baseline activity" is defined as the mobile source's level of activity during
the applicable mobile source baseline year. The definition for "Mobile source
baseline emissions" is a source's total actual mobile source emissions based
on the mobile source activity and the mobile source emissions rate. "Most
stringent allowable emissions rate" is the emission rate of a source, considering
all limitations required by applicable local, state, and federal regulations.
The term "Strategy activity" is the source's level of activity during the
discrete emission reduction generation period and "Strategy emission rate"
is the source's emission rate during the discrete emission reduction generation
period. "Source" is a point of origin of air contaminants, whether privately
or publically owned or operated. Upon request of a source owner, the executive
director shall determine whether multiple processes emitting air contaminants
from a single point of emission will be treated as a single source or multiple
sources.
New §101.371 states that the purpose of Division 4 is to allow an
operator of a source to generate and use discrete emission credits. The wording
of this section is revised from the previous language in §101.29 to refer
to both DERCs and MDERCs as discrete emission credits, unless the rule language
refers to specifically only one of these discrete emission credits. This new
section also states that participation in the program is voluntary.
New §101.372 contains the general provisions for the Discrete Emission
Credit and Trading Program. The wording of this section is revised from the
previous language in §101.29 to refer to both DERCs and MDERCs as emission
credits, unless the rule language refers to only one of these discrete emission
credits. The section specifies to which pollutants the program will apply
and the included pollutants are unchanged from those previously in §101.29.
Language was added to clarify that the EPA must also grant approval before
a reduction of one pollutant may be used to meet the requirements of another
pollutant. The section states that DERCs and MDERCs must be real, quantifiable,
and surplus. The certification requirements of a discrete emission credit
would be revised to only allow credits which have occurred after the most
recent year of emissions inventory used for SIP determinations and to require
the source's annual emissions prior to the submittal of the emission credit
application to have been represented in the emissions inventory of the most
recent year of emissions inventory used for SIP determinations. Rule language
is added which prohibits emission credits certified as DERCs or MDERCs from
being recertified as emission credits under any other division within Subchapter
H. The section allows for stationary sources (including area sources), mobile
sources, and stationary sources (including area sources) or mobile sources
associated with agencies under §101.30 to be eligible to generate and
use emission credits. The rule language will allow DERCs and MDERCs to be
available for use after the executive director has received a notice of generation
and the discrete emission credits have been reviewed and deemed creditable.
This is a change from previous procedures where emission credits were placed
in the registry upon receipt of the notice of generation and were not reviewed
for credibility until a notice of intent to use was received by the executive
director. This change will allow for the emission reduction program and the
discrete emission reduction program to operate on a more consistent basis.
The section states that DERCs and MDERCs may be used anytime after certification
and that they do not expire. The geographic scope will remain the same as
previously stated in §101.29, except the new rule language will allow
for the trading and use of emission credits generated in other counties, states,
or nations provided that a demonstration has been made and approved by the
executive director and the EPA showing that the reduction in the area where
the credit was generated causes an improvement in air quality in the county
where the credit is used. As previously stated in §101.29, the trading
of discrete emission credits may be discontinued by the executive director
with commission approval, and for areas having an ozone season less than 12
months, discrete emission credits generated outside the ozone season may not
be used during the ozone season. The commission will maintain a registry that
lists all discrete emission credits available or used. The section requires
the generator and user of discrete emission credits to maintain a copy of
records for a minimum of five years regarding the generation and use of credits.
The records shall include at a minimum the name, emission point, and facility
identification number of each source using discrete reduction credits, the
amount of discrete reduction credits being used, and the specific identification
number of the credit being used. As previously stated in §101.29, all
information submitted with any application to generate or use discrete emission
credits may not be submitted as confidential and discrete emission credits
do not constitute a property right. The rules state that the executive director
has the authority to prohibit either the generation or the use of discrete
reduction credits if the executive director determines that the company has
violated any of the requirements of the program or has abused the privileges
provided by the program. Rule language concerning the start date for the discrete
emission reduction program has been removed, since this program is currently
ongoing.
New §101.373 outlines the required protocols of generating, calculating,
certifying and registering, using, and transferring discrete emission credits.
This section requires discrete emission credits to be determined based on
established EPA protocols when available, actual monitoring results, or calculated
using good engineering practices. There are no changes from the previous requirements
in §101.29 regarding the various means for generating discrete emission
credits. The section revises the equation for calculating the amount of DERCs
generated to use the lower of the baseline emission rate or the most stringent
emission rate. This revision will allow for the correct calculation of DERCs
if the baseline emission rate was exceeding the emission rate required by
local, state, or federal requirements. As previously in §101.29, the
section would require DERCs to be rounded down to the nearest ton. The section
limits the generation period for DERCs to five years. The section would not
allow a source to generate discrete emission credits for any emissions exceeding
its allowable emission limit. The section deletes a requirement that previously
existed in §101.29, which restricted reductions used for netting from
being generated as DERCs. The new section states what requirements and data
must be documented to calculate MDERCs.
The language previously located in §101.29 regarding registration
and certification of emission credits remains the same and is relocated to §101.373.
The section adds language detailing what information, at a minimum, would
be required to generate mobile discrete emission credits. The information,
which is to be submitted on DEC-1 Form, includes the information necessary
for the executive director to review the application in accordance with the
new rules and to properly administer the program. It should be noted that,
for continuing credits, each application will be reviewed for creditability
at the time of submittal in addition to the time of strategy implementation.
The new rule language specifically states the commission's practice that discrete
emissions credits will be determined and certified to the nearest ton. The
section includes new language regarding the review of discrete emission reduction
registrations for credibility upon receipt and that applicants being denied
registration of discrete emission credits would be notified of such denial
in writing. The section states that discrete emission credits will be reviewed
and certified based on actual monitoring data, EPA methodology, or other commission
approved protocols. In addition, rule language is added which states that
discrete emission credits will be deposited in the registry and will be available
for use until they are used, withdrawn, or expire. The compliance and burden
language is essentially the same as formerly stated in §101.29. The user
would be responsible for ensuring that the discrete emission credits are certified
and certification, by the executive director, does not relieve the user on
any other responsibilities. Previously existing §101.29 language regarding
what discrete emissions can or cannot be used for has been reorganized into
subparagraphs which state what the discrete emission credits can be used for
and a subparagraph which states what they cannot be used for.
The adoption relocates the equations which provide flexibility to the 30-day
rolling average emission limits and the new maximum daily emission limit for
source caps as defined in Chapter 117 from §101.29 to new §101.373.
The commission modified the equation used to calculate the amount of discrete
emission credits needed to demonstrate compliance or meet a regulatory requirement
to be consistent with the terms adopted for this division, and added language
which would be consistent with the procedures and methodologies adopted within
this division.
The equations for calculating 30-day rolling average emission limits are
relocated from §101.29 to §101.373 unmodified. There are no changes
to the existing requirements for additional credits needed as compliance margins
or for environmental contributions. As previously stated in §101.29,
the calculated discrete emission credits will be rounded up to the nearest
ton and the user must retire 10% more than are needed. The amount of discrete
emission credits needed for NSR offsets would remain equal to the quantity
of tons needed to achieve the maximum allowable emission level set in the
user's NSR program. As previously stated in §101.29, discrete emission
credits which are not used during the use period would remain surplus and
available for use or transfer by the holder. As previously stated in §101.29,
a notice of intent to use the DEC-2 Form would be submitted to inform the
executive director of the intent to use discrete emission credits. The information
required to be submitted on the DEC-2 Form would remain the same as previously
stated in §101.29. The section includes a list of the required information
to be submitted when a mobile source user intends to use discrete emission
credits. The requirement for a user to notify the executive director of the
amount of actual discrete emission credit use remains the same as previously
stated in §101.29 with the exception of added language requiring the
user to submit the information on a DEC-3 Form. The language regarding compliance
burden and enforcement for discrete emission credit users is transferred unchanged
from §101.29.
New §101.374 is a relocation of requirements from §101.29, with
no changes, concerning auditing of the DERC program. The word "section" as
found in proposed §101.374(a) was replaced with "division" since the
intent was to refer to the entire Division 4 and not §101.374.
FINAL REGULATORY IMPACT ANALYSIS DETERMINATION
The commission has reviewed the adopted rulemaking in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225. Divisions
1 and 4 create a voluntary mechanism which provides regulatory flexibility
for compliance with state and federal emission limitations and do not add
mandatory regulatory requirements or required costs. Division 3 affects owners
and operators of new and existing stationary sources emitting NO
x
subject to §§117.106, 117.206, and 117.475 requirements
in the HGA nonattainment area. The commission has determined the adopted rulemaking
in Division 3 of Chapter 101 meets the definition of a "major environmental
rule" as defined in Texas Government Code, §2001.0225, but adopted rulemaking
in Divisions 1 and 4 does not. "Major environmental rule" means a rule, the
specific intent of which, is to protect the environment or reduce risks to
human health from environmental exposure, and that may adversely affect in
a material way the economy, a sector of the economy, productivity, competition,
jobs, the environment, or the public health and safety of the state or a sector
of the state.
The adopted rules do not meet any of the four applicability criteria for
requiring a regulatory analysis of "major environmental rule" as defined in
the Texas Government Code. Section 2001.0225 applies only to a major environmental
rule the result of which is to: 1) exceed a standard set by federal law, unless
the rule is specifically required by state law; 2) exceed an express requirement
of state law, unless the rule is specifically required by federal law; 3)
exceed a requirement of a delegation agreement or contract between the state
and an agency or representative of the federal government to implement a state
and federal program; or 4) adopt a rule solely under the general powers of
the agency instead of under a specific state law.
As discussed earlier in this preamble, these adoptions are one element
of the control strategy for the HGA SIP. Adoption and implementation of this
control strategy is necessary in order for the HGA nonattainment area to comply
with the requirements of the FCAA and achieve attainment for ozone. Additional
elements of the control strategy for the HGA SIP are being adopted concurrently
in this issue of the
Texas Register
, or were
included in the HGA SIP considered by the commission on December 6, 2000,
and planned to be submitted to the EPA by December 31, 2000.
Under the cap and trade portion of these rules, existing sources would
be limited to NO
x
emission levels under an emissions
cap based on historical operating data and source specific emission rates
determined by Chapter 117. New stationary sources would be required to identify
a source(s) of allowances equal to allowable emissions prior to commencing
operation. All sources subject to this division would be required to hold
a quantity of allowances in their compliance account by February 1 following
the end of a control period, which is equal to or greater than the total emissions
from the preceding control period. The cost of allowances in similar programs
nationwide has ranged from approximately $500 to $5,000 per allowance (ton),
depending on availability and demand. Actual costs in the HGA nonattainment
area will be dependent upon market demand and availability. The commission
is proposing these sections as part of a strategy to reduce and permanently
cap emissions of NO
x
to a level which would allow
the HGA nonattainment area to attain the NAAQS for ozone. This is based on
the analysis provided in the rule proposal preamble which was published in
the August 25, 2000 issue of the
Texas Register
(25 TexReg 8137), including the discussion in the Public Benefit and Costs
section.
These rules do not exceed an express standard set by federal law, since
they implement requirements of the FCAA. Provisions of 42 USC, §7410,
require states to adopt a SIP which provides for "implementation, maintenance,
and enforcement" of the primary NAAQS in each air quality control region of
the state. These rules were specifically developed as part of an overall control
strategy to meet the ozone NAAQS set by the EPA under 42 USC, §7409.
While 42 USC, §7410 does not require specific programs, methods, or reductions
in order to meet the standard, state SIPs must include "enforceable emission
limitations and other control measures, means or techniques (including economic
incentives such as fees, marketable permits, and auctions of emissions rights),
as well as schedules and timetables for compliance as may be necessary or
appropriate to meet the applicable requirements of this chapter," (meaning
the FCCA, Chapter 85, Air Pollution Prevention and Control). It is true that
the FCAA does require some specific measures for SIP purposes, like the inspection
and maintenance program, but those programs are the exception, not the rule,
in the SIP structure of the FCAA. The provisions of the FCAA recognize that
states are in the best position to determine what programs and controls are
necessary or appropriate in order to meet the NAAQS. This flexibility allows
states, affected industry, and the public, to collaborate on the best methods
for attaining the NAAQS for the specific regions in the state. Even though
the FCAA allows states to develop their own programs, this flexibility does
not relieve a state from developing a program that meets the requirements
of 42 USC, §7410. In order to avoid federal sanctions, states are not
free to ignore the requirements of 42 USC, §7410 and must develop programs
to assure that the nonattainment areas of the state will be brought into attainment
on schedule. Thus, while specific measures are not prescribed, both a plan
and emission reductions are required to assure that the nonattainment areas
of the state will be able to meet the attainment deadlines set by the FCAA.
The EPA has provided the criteria for both the submission and evaluation of
attainment demonstrations developed by states to comply with the FCAA. This
criteria requires states to provide, in addition to other information, photochemical
modeling and an analysis of specific emission reduction strategies necessary
to attain the NAAQS. The commission's photochemical modeling and other analysis
indicate that substantial emission reductions from both mobile and point source
categories are necessary in order to demonstrate attainment. In this case,
this rulemaking is intended to achieve reductions in ozone precursor emissions
in the HGA nonattainment area. Specifically, as noted elsewhere in this rule
preamble, the emission reductions associated with these rules are a necessary
element of the attainment demonstration required by the FCAA.
In addition, 42 USC, §7502(a)(2), requires attainment as expeditiously
as practicable, and 42 USC, §7511a(d), requires states to submit ozone
attainment demonstration SIPs for severe ozone nonattainment areas such as
HGA. By policy, the EPA requires photochemical grid modeling to demonstrate
whether the 42 USC, §7511a(f), NO
x
measures
would contribute to ozone attainment. The commission has performed photochemical
grid modeling which predicts that NO
x
emission
reductions, such as those required by these rules, will result in reductions
in ozone formation in the HGA ozone nonattainment area and help bring HGA
into compliance with the air quality standards established under federal law
as NAAQS for ozone. The 42 USC, §7511a(f), exemption from NO
x
measures for HGA expired on December 31, 1997. The expiration of
the exemption under 42 USC, §7511a(f), was based on the finding that
NO
x
reductions in HGA are necessary for attainment
of the ozone standard. Therefore, the adopted amendments are necessary components
of and consistent with the ozone attainment demonstration SIP for HGA, required
by 42 USC, §7410.
During the 75th Legislative Session, Senate Bill (SB) 633 amended the Texas
Government Code to require agencies to perform a regulatory impact analysis
of certain rules. The intent of SB 633 was to require agencies to conduct
a RIA of extraordinary rules. With the understanding that this requirement
would seldom apply, the commission provided a cost estimate for SB 633 that
concluded "based on an assessment of rules adopted by the agency in the past,
it is not anticipated that the bill will have significant fiscal implications
for the agency due to its limited application." The commission also noted
that the number of rules that would require assessment under the provisions
of the bill was not large. This conclusion was based, in part, on the criteria
set forth in the bill that exempted proposed rules from the full analysis
unless the rule was a major environmental rule that exceeds a federal law.
As previously discussed, the FCAA does not require specific programs, methods,
or reductions in order to meet the NAAQS; thus, states must develop programs
for each nonattainment area to ensure that area will meet the attainment deadlines.
Because of the ongoing need to address nonattainment issues, the commission
routinely proposes and adopts SIP rules. The legislature is presumed to understand
this federal scheme. If each rule adopted for inclusion in the SIP was considered
to be a major environmental rule that exceeds federal law, then every SIP
rule would require the full RIA contemplated by SB 633. This conclusion is
inconsistent with the conclusions reached by the commission in its cost estimate
and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature
is presumed to understand the fiscal impacts of the bills it passes, and that
presumption is based on information provided by state agencies and the LBB,
the commission believes that the intent of SB 633 was only to require the
full RIA for rules that are extraordinary in nature. While the SIP rules will
have a broad impact, that impact is no greater than is necessary or appropriate
to meet the requirements of the FCAA.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
It is presumed that "when an agency interpretation is in effect at the time
the legislature amends the laws without making substantial change in the statute,
the legislature is deemed to have accepted the agency's interpretation."
The commission's interpretation of the RIA requirements is also supported
by a change made to the Administrative Procedure Act (APA) by the legislature
in 1999. In an attempt to limit the number of rule challenges based upon APA
requirements, the legislature clarified that state agencies are required to
meet these sections of the APA against the standard of "substantial compliance."
Texas Government Code, §2001.035.The legislature specifically identified
Texas Government Code, §2001.0225 as falling under this standard. The
commission has substantially complied with the requirements of §2001.0225.
Therefore, in addition to not exceeding an express standard set by federal
law, the rules do not exceed state requirements, and are not adopted solely
under the general powers of the agency because the provisions of the TCAA, §§382.011,
382.012, and 382.017 authorize the commission to implement a plan for the
control of the states air quality, including measures necessary to meet federal
requirements. The remaining applicability criteria, pertaining to exceeding
a delegation agreement or contract between the state and the federal government
does not apply. Thus, the commission is not required to conduct a regulatory
analysis as provided in Texas Government Code, §2001.0225.
Comments received during the comment period regarding the draft RIA are
addressed in the ANALYSIS OF TESTIMONY section of this preamble.
TAKINGS IMPACT ASSESSMENT
The commission evaluated this rulemaking action and performed an analysis
of whether the rules are subject to Texas Government Code, Chapter 2007. The
following is a summary of that analysis. These sections are adopted as part
of a strategy to reduce and permanently cap emissions of NO
x
to a level which would allow the HGA nonattainment area to attain
the NAAQS for ozone. Promulgation and enforcement of the rules will not burden
private real property. The new sections do not affect private property in
a manner which restricts or limits an owner's right to the property that would
otherwise exist in the absence of a governmental action. Additionally, the
credits and allowances created under these rules are not property rights.
Consequently, these sections do not meet the definition of a takings under
Texas Government Code, §2007.002(5).
Also, Texas Government Code, §2007.003(b)(13), states that Chapter
2007 does not apply to an action that: 1) is taken in response to a real and
substantial threat to public health and safety; 2) is designed to significantly
advance the health and safety purpose; and 3) does not impose a greater burden
than is necessary to achieve the health and safety purpose. Although the rule
revisions do not directly prevent a nuisance or prevent an immediate threat
to life or property, they do prevent a real and substantial threat to public
health and safety, and significantly advance the health and safety purpose.
In addition, §2007.003(b)(4) provides that Chapter 2007 does not apply
to the adopted rules since they are reasonably taken to fulfill an obligation
mandated by federal law. Specifically, the emission limitations and control
requirements within this adoption were developed in order to meet the ozone
NAAQS set by the EPA under the FCAA, §7409. States are primarily responsible
for ensuring attainment and maintenance of the NAAQS once the EPA has established
them. Under the FCAA, §7410 and related provisions, states must submit,
for approval by the EPA, SIPs that provide for the attainment and maintenance
of NAAQS through control programs directed to sources of the pollutants involved.
Therefore, the purpose of the rule adoption is to implement a NO
x
strategy which is necessary for the HGA area to meet the air quality
standards established under federal law as NAAQS. This action is taken in
response to the HGA area exceeding the NAAQS for ground-level ozone, which
adversely affects public health, primarily through irritation of the lungs.
The action significantly advances the health and safety purpose by reducing
ambient NO
x
and ozone levels in HGA. Attainment
of the ozone standard will eventually require substantial NO
x
reductions. Any NO
x
reductions resulting
from the current rulemaking are no greater than what the best scientific research
indicates is necessary to achieve the desired ozone levels. However, this
rulemaking is only one step among many necessary for attaining the ozone standard.
Consequently, the exemption which applies to these rules is that of an action
reasonably taken to fulfill an obligation mandated by federal law. Therefore,
these revisions do not constitute a takings under Texas Government Code, Chapter
2007.
The commission has included elsewhere in this preamble its reasoned justification
for adopting this strategy and has explained why it is a necessary component
of the SIP, which is federally mandated. This discussion, as well as the HGA
SIP which is being adopted concurrently, explains in detail that every rule
in the HGA SIP package is necessary and that none of the reductions in those
packages represent more than is necessary to bring the area into attainment
with the NAAQS. For these reasons the rules do not constitute a takings under
Chapter 2007 and do not require additional analysis.
Comments received during the comment period regarding the takings impact
assessment (TIA) are addressed in the ANALYSIS OF TESTIMONY section of this
preamble.
COASTAL MANAGEMENT PROGRAM CONSISTENCY REVIEW
The commission has determined that this rulemaking action relates to an
action or actions subject to the Texas Coastal Management Program (CMP) in
accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural
Resources Code, §§33.201
et seq.
),
and the commission's rules in 30 TAC Chapter 281, Subchapter B, concerning
Consistency with the Texas Coastal Management Program. As required by 30 TAC §281.45(a)(3)
and 31 TAC §505.11(b)(2), relating to actions and rules subject to the
CMP, commission rules governing air pollutant emissions must be consistent
with the applicable goals and policies of the CMP. The commission has reviewed
this action for consistency with the CMP goals and policies in accordance
with the regulations of the Coastal Coordination Council, and has determined
that the adopted rules are consistent with the applicable CMP goal expressed
in 31 TAC §501.12(1) of protecting and preserving the quality and values
of coastal natural resource areas, and the policy in 31 TAC §501.14(q),
which requires that the commission protect air quality in coastal areas. If
adopted, the new sections will reduce and cap emissions of NO
x
in the HGA nonattainment area to a level that would allow attainment
of the NAAQS for ozone. No new contaminants will be authorized by these rules,
and a reduction of NO
x
emissions should occur.
Comments received during the comment period regarding the Coastal Management
Program Consistency Review are addressed in the ANALYSIS OF TESTIMONY section
of this preamble.
EFFECT ON SITES SUBJECT TO THE FEDERAL OPERATING PERMIT PROGRAM
The new sections under Divisions 1, 3, and 4, will become part of the state's
ozone attainment strategy; therefore, these amendments will be submitted as
part of the SIP. As a result, the new sections and any allowances allocated
under these sections would become applicable requirements under the federal
operating permit program.
HEARINGS AND COMMENTERS
The commission held public hearings on this adoption at the following locations:
September 18, 2000, in Conroe and Lake Jackson; September 19, 2000 in Houston
(TWO hearings); September 20, 2000, in Katy and Pasadena; September 21, 2000,
in Beaumont, Amarillo, and Texas City; September 22, 2000, in Dayton, El Paso,
and Arlington; and September 25, 2000, in Austin and Corpus Christi. The comment
period closed at 5:00 p.m. on September 25, 2000. The following commenters
provided oral testimony and/or submitted written testimony: Avista-Steag,LLC
(Avista-Steag), BASF Corporation (BASF), Business Coalition for Clean Air
(BCCA), Calpine Central LP (Calpine), Chevron Phillips Chemical Company (Chevron),
City Public Service of San Antonio (CPS), City of Spring Valley (Spring Valley),
Clean Air Action Corporation (CAAC), Coalition for Gas-Based Environmental
Solutions (Coalition), Diamond Koch (Diamond-Koch), Dow Chemical Company
(Dow), Dynegy, Inc. (Dynegy), Enron Corporation (Enron), Entergy Services,
Inc. (Entergy), Enterprise Products Operating, LP (Enterprise), Environmental
Defense (ED), Equistar Chemicals, LP (Equistar), ExxonMobile Corporation
(ExxonMobile), FPL Energy (FPL), Fuel Tech, Inc, (Fuel Tech), Gas Processors
Association (GPA), Goodyear Tire and Rubber Company (Goodyear), Houston Galveston
Area Council (HGAC), Houston Metropolitan Planning Organization's Transportation
Policy Council (The Council), Kinder Morgan, Inc. (Kinder Morgan), League
of Women Voters of Texas (LWV-TX), Lyondell Chemical Company (Lyondell), Lyondell-Citgo
Refining, LP. (LCR), National Aeronautics and Space Administration (NASA),
Pasadena Paper (Pasadena), Peco Energy Company (Peco), Phillips 66 Company
(Phillips 66), Printing and Image Association of Texas (PIAT), RMT, Inc. (RMT),
Regional Air Quality Consensus Group (RAQCG), Reliant Energy, Inc. (Reliant),
Sierra Club Houston Regional Group (Sierra-Houston), Solutia (Solutia), Stolt-Nielsen
Transportation Group Ltd. (SNTG), Texas Industrial Project (TIP) via Baker
Botts, LLP, TXI Operations, LP. (TXI), TXU Business Services (TXU), Tennessee
Gas Pipeline Company (TGP), Texas Chemical Council (TCC), Texas Eastern Transmission
Corporation (Texas Eastern), Texas Oil and Gas Association (TxOGA), Texas
Pulp and Paper Industry Environmental Council (TPIEC), Trunkline Gas Company
(TGC), U.S. Environmental Protection Agency (EPA), Valero Refining Company-Texas
(Valero) and twenty three individuals. The companies and organizations expressed
general support for the cap and trade concept but opposed many parts of the
proposed implementation and suggested changes. These comments are detailed
under ANALYSIS OF TESTIMONY. Fifteen individuals opposed the cap and trade
concept. Eight individuals expressed general support for the cap and trade
concept.
ANALYSIS OF TESTIMONY
Baker Botts commented that it generally supports the ongoing efforts by
the commission to develop a SIP that is technologically achievable, economically
reasonable, and legally approvable. Baker Botts, BCCA, Dynegy, Equistar, ExxonMobil,
Goodyear, Harris County Judge Robert Eckels, Phillips 66, TCC, TPIEC, TxOGA,
Valero, and an individual commented that the commission should incorporate
into the SIP a greater level of reductions from federally preempted sources
and stated that EPA-regulated sources account for about 40% of the NO
The rule has not been revised based on these comments. The commission agrees
with the commenters that emission reductions from federally preempted sources
would provide benefits for the HGA SIP demonstration, and the inability of
the commission to regulate certain source categories has necessitated the
use of other ozone control strategies. However, the commission understands
that the EPA SIP approval process does not provide a mechanism for credit
for emission reductions that occur after the attainment date. The commission
understands that the EPA is not currently considering accelerating implementation
schedules for existing federal rules. The commission is working with the EPA
to determine the availability of SIP credit for many non-traditional control
strategy mechanisms, like economic incentive programs and flexibility for
preempted source categories. Additionally, the commission is working with
the EPA to determine an appropriate federal contribution credit available
for the HGA SIP.
BCCA, Entergy, Equistar, ExxonMobil, Goodyear, GPA, Kinder Morgan, Lyondell,
PECO, Phillips 66, REI, TPIEC, and TXI, commented on the draft RIA and stated
that the proposed rules were not evaluated in accordance with the analysis
requirements for a major environmental rule. The commenters stated that Texas
Government Code, §2001.0225, requires an RIA for certain major environmental
rules. The commenters stated that the commission must consider the benefits
and costs of the proposed rules in relationship to state agencies, local governments,
the public, the regulated community, and the environment. The commenters stated
further that the commission must also incorporate aspects of this analysis
into the fiscal note in the proposed rules (e.g., identify the costs and the
benefits; describe reasonable alternative methods for achieving the purpose
of the rules considered by the agency; provide the reasons for rejecting those
alternatives; and identify the data and methodology used in performing the
analysis). The commenters stated that under §2001.0225(d) the commission
must also find that "compared to the alternative proposals considered and
rejected, the rule will result in the best combination of effectiveness in
obtaining the desired results and of economic costs not materially greater
than the costs of any alternative regulatory method considered."
The commenters stated that the rule proposal preamble's statement that
the rules are exempt from the RIA requirement because federal law mandates
the rules is a legally flawed effort to avoid an RIA and may render the rules
invalid. The commenters stated that federal law does not mandate the control
requirements, emission rates, and use restrictions contained in the proposal
and asserted that many of the proposed rules exceed specific federal rules
and standards applicable to the same sources. The commenters stated that examples
of departures from the federal framework include the following: boiler, turbine
and other fired equipment emission limits set well below federal new source
performance standards (NSPS), RACT, best available control technology (BACT),
or lowest achievable emission rate (LAER) limits for the same sources; and
compressor engine emission limits set at unprecedented low levels specifically
designed to be unachievable and prevent the further use of the affected engines.
TXI stated that the NAAQS does not provide in and of themselves any standards
applicable to the regulated community, and that a state with an approved SIP
has broad flexibility on how to meet the NAAQS. TXI stated that the commission
failed to cite "an 'express requirement of state law' that justifies the promulgation
of the proposed rule without complying with the mandates of §2001.0225."
TXI stated that none of the state laws cited in the rule proposal preamble
(TCAA, §§382.011, 382.012, and 382.017) is "an 'express requirements
of state law' to adopt these NO
x
emission rules."
TXI commented that
The Senate Natural Resources
Committee, Interim Report to the 75th Legislature, Use of Cost Benefit Analysis
in Environmental Regulation
(September 1996) regarding §2001.0225
states on page-eight that "The heightened scrutiny approach would be applied
only to the environmental regulations that are
not
specifically required
by federal law, a federally- delegated program
agreement or an express requirement of state law. Obviously, if the agency
has
no discretion about whether to adopt regulations
, it should not be required to prepare a heightened scrutiny document."
(TXI's emphasis added)
TXI stated that the commission must quantify the costs associated with
the proposal either for the purpose of determining the reasonableness of the
proposed NO
x
controls for achieving the commission's
desired result or for complying with the specified requirements of §2001.0225.
TXI asserted that the commission did not perform a study of the costs associated
with the proposed rule for lightweight aggregate kilns. TXI also asserted
that the commission did not perform a quantitative analysis of the estimated
cost to the Texas lightweight aggregate industry and that without such an
analysis, the commission cannot determine the reasonableness of the proposed
rule from an economic perspective.
The commenters stated that the rule proposal preamble acknowledges that
the rule proposal's components are "major environmental rules," but that the
commission asserted that an RIA is "seldom" required and is only required
for "extraordinary" rules. The commenters stated that these criteria appear
nowhere in the RIA requirements. The commenters stated that the rule proposal
preamble states that "while the SIP rules will have a broad impact, that impact
is no greater than is necessary or appropriate to meet the requirements of
the FCAA." The commenters stated that this "no greater than is necessary or
appropriate" determination is the conclusion that an RIA is designed to evaluate
and to offer for public review and comment. The commenters stated that the
rule proposal is well beyond any federal mandates for the covered sources
and are "extraordinary." The commenters stated that under Texas Government
Code, §2001.0225, an RIA must be performed and offered for public comment
before the proposal can be adopted.
The rules have not been revised based on these comments. The commission
agrees that the cap and trade portion of the rules meets the definition of
a major environmental rule; however, the commission disagrees that its interpretation
of the exemption for federally mandated standards is legally flawed. While
the rules may limit growth of emissions from point sources in the HGA nonattainment
area, that alone is not enough to trigger the RIA requirements. Texas Government
Code, §2001.0225 only applies to a major environmental rule adopted by
a state agency, the result of which is to: 1) exceed a standard set by federal
law, unless the rule is specifically required by state law; 2) exceed an express
requirement of state law, unless the rule is specifically required by federal
law; 3) exceed a requirement of a delegation agreement or contract between
the state and an agency or representative of the federal government to implement
a state and federal program; or 4) adopt a rule solely under the general powers
of the agency instead of under a specific state law.
This rulemaking action does not meet any of these four applicability requirements,
and is adopted in substantial compliance with the RIA requirements. Texas
Government Code, §2001.035. This rule does not exceed an express standard
set by federal law because the cap and trade rules are specifically developed
to meet the ozone NAAQS set by the EPA under 42 USC, §7409. Title 42
USC, §7410 requires states to adopt a SIP which provides for "implementation,
maintenance, and enforcement" of the primary NAAQS in each air quality control
region of the state. While 42 USC, §7410 does not specifically prescribe
programs, methods, or reductions to meet the federal standard, state SIPs
must include "enforceable emission limitations and other control measures,
means or techniques (including economic incentives such as fees, marketable
permits, and auctions of emissions rights), as well as schedules and timetables
for compliance as may be necessary or appropriate to meet the applicable requirements
of this chapter" (meaning FCAA, Chapter 85, Air Pollution Prevention and Control).
The FCAA does require some specific measures for SIP purposes, such as an
inspection and maintenance program, but those programs are the exception,
not the rule, in the federal SIP structure. The provisions of the FCAA recognize
that states are in the best position to determine what programs and controls
are necessary or appropriate in order to meet the NAAQS. This flexibility
allows states, affected industry, and the public, to collaborate on the best
methods for attaining the NAAQS for the specific regions in the state. In
order to avoid federal sanctions, states are not free to ignore the requirements
of 42 USC, §7410, and must develop programs to assure that the nonattainment
areas of the state will be brought into attainment on schedule. Failure to
develop control strategies to demonstrate attainment can result in federal
sanctions. Thus, while specific measures are not prescribed, both a plan and
emission reductions are required to assure that the nonattainment areas of
the state will be able to meet the attainment deadlines set by the FCAA. The
EPA has provided the criteria for both the submission and evaluation of attainment
demonstrations developed by States to comply with the FCAA. This criteria
requires states to provide, in addition to other information, photochemical
modeling and an analysis of specific emission reduction strategies necessary
to attain the NAAQS. The commissions photochemical modeling and other analysis
indicates that substantial emission reductions from both mobile and point
source categories are necessary in order to demonstrate attainment. In this
case, this rulemaking is intended to achieve reductions in ozone emissions
in the HGA nonattainment areas. Specifically, as noted elsewhere in this rule
preamble, the emission reductions associated with this rule are a necessary
element of the attainment demonstration required by the FCAA.
This conclusion is supported by the legislative history for Texas Government
Code, §2001.0225. During the 75th Legislative Session, Senate Bill (SB)
633 amended the Texas Government Code to require agencies to perform a regulatory
impact analysis of certain rules. The intent of SB 633 was to require agencies
to conduct a RIA of major environmental rules that will have a material adverse
impact, and will exceed a requirement of state law, federal law, or a delegated
federal program, or are adopted solely under the general powers of the agency.
The commission provided a cost estimate for SB 633 that concluded "based on
an assessment of rules adopted by the agency in the past, it is not anticipated
that the bill will have significant fiscal implications for the agency due
to its limited application." The commission also noted that the number of
rules that would require assessment under the provisions of the bill was not
large. Because of the ongoing need to address nonattainment demonstrations
required by federal law, the commission routinely proposes and adopts SIP
rules. If each rule proposed for inclusion in the SIP was incorrectly considered
as exceeding federal law, every SIP rule would require the full RIA contemplated
by SB 633. This result would be inconsistent with the cost estimates and fiscal
notes prepared by the commission and by the Legislative Budget Board (LLB).
Since the legislature is presumed to understand the fiscal impacts of the
bills it passes, and that presumption is based on information provided by
state agencies and the LBB, the commission believes that the intent of SB
633 was only to require the full RIA for rules that meet the requirements
under §2001.0225(a). While the SIP rules will have a broad impact, that
impact is no greater than is necessary or appropriate to meet the requirements
of the FCAA. In other words, the proposed rule is intended to meet federal
and state law, and does not go above and beyond what is required to meet federal
or state statutes.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
It is presumed that "when an agency interpretation is in effect at the time
the legislature amends the laws without making substantial change in the statute,
the legislature is deemed to have accepted the agency's interpretation."
The commission's interpretation of the RIA requirements is also supported
by a change made to the Administrative Procedure Act (APA) by the Legislature
in 1999. In an attempt to limit the number of rule challenges based upon APA
requirements, the legislature clarified that state agencies are required to
meet these sections of the APA against the standard of "substantial compliance."
Texas Government Code, §2001.035. The legislature specifically identified §2001.0225
as falling under this standard. The commission has substantially complied
with the requirements of §2001.0225.
Therefore, in addition to not exceeding an express standard set by federal
law, this rulemaking does not exceed state requirements, and is not adopted
solely under the general powers of the agency because the provisions of the
TCAA, §§382.011, 382.012, and 382.017 authorize the commission to
implement a plan for the control of the states air quality, including measures
necessary to meet federal requirements. The remaining applicability criteria,
pertaining to exceeding a delegation agreement or contract between the state
and the federal government does not apply. Thus, the commission is not required
to conduct a regulatory analysis as provided in Texas Government Code, §2001.0225.
BCCA, Entergy, ExxonMobil, Equistar, Goodyear, Lyondell, Phillips 66, REI,
and TPIEC stated that the proposed rules did not include an adequate TIA as
required under Texas Government Code, §2007, with Goodyear stating that
the proposal amounts to a taking of its engines (including a recently retrofitted
engine) "not supported by adequate scientific support, public participation,
or legal process." The commenters stated that the TIA provision mandates that
covered agencies "take a 'hard look' at the private real property implications
of the actions they undertake...," according to the Office of the Attorney
General,
Private Real Property Rights Preservation
Act Guidelines
, (January 12, 1996 issue of the
Texas Register
(21 TexReg 387)). The commenters stated that under §2007.043,
a TIA must describe the specific purpose of the proposed action, determine
whether engaging in the proposed governmental action will constitute a taking,
and describe reasonable alternative actions that could accomplish the specified
purpose. The commenters stated that the agency must also explain whether these
alternative actions also would constitute takings.
The commenters stated that agencies must also comply with guidelines developed
by the Texas Attorney General when developing the TIA and that according to
these guidelines, agencies must carefully review governmental actions that
have a significant impact on the owner's economic interest. The commenters
stated that these guidelines include the statement: "Although a reduction
in property value alone may not be a 'taking,' a severe reduction in property
value often indicates a reduction or elimination of reasonably profitable
uses." (January 12, 1996 issue of the
Texas Register
(21 TexReg 392)). The commenters stated that examples of aspects of
the rule proposal that could significantly impact private real property in
a manner that constitutes a taking include gas-fired compressor engines and
other point source NO
x
controls. The commenters
stated that the rule proposal preamble acknowledged that retrofitting compressor
engines to the level specified in the proposal is infeasible (25 TexReg 8137
and 8291), and stated that the existing equipment, representing a significant
capital improvement at a number of industrial sites, would be rendered unusable.
The commenters stated that the 90% point source reduction requirement is economically
and technologically infeasible for a number of existing sites, and that this
requirement could cause a number of facilities to shut down their operations,
dramatically impacting the value of their real property.
The commenters stated that the proposed rule preamble acknowledged that
some of the rules may "burden" private real property but claimed an exemption
from performing a TIA based on the assertion that the proposal does not impose
a greater burden than necessary to advance a health and safety purpose and
that the proposal "reasonably" fulfills a federal mandate. (25 TexReg 8175,
8194, 8201, 8208, 8220, 8228, 8237, 8245, 8294, and 8295). The commenters
stated that the commission provided the public no basis to infer that a cost/benefit
analysis or a reasonableness determination was, in fact, performed as necessary
to support the TIA exemption claim because the preamble contains only the
bare assertions. The commenters asserted that the proposed rules will impose
a greater burden than is necessary, and are not reasonably taken to fulfill
a federal mandate. The commenters commented that according to the Attorney
General's Guidelines, a full TIA was required to be completed with the proposal,
and that failure to perform a TIA could invalidate the rules.
The rules have not been revised based on these comments. The primary reason
the commission determined that these rules did not constitute a takings under
Texas Government Code, Chapter 2007 is that it will not burden private real
property. The allowances created under these rules, like other authorizations
to emit, are not property rights and therefore cannot be the basis for a takings
claim. Generally, these rules themselves should not impose any requirements
on point sources, but only requirements of recordkeeping and reporting. In
fact, these rules provide flexibility for meeting the requirements of the
revisions to Chapter 117 regarding NO
x
reductions
from point sources in the HGA nonattainment area which are adopted concurrent
with this rulemaking. To the extent that the commenters are concerned about
takings implications of the requirements of the Chapter 117 rule revisions,
they may review the response to this comment in the preamble for those rule
revisions which are published elsewhere in this version of the
Texas Register
.
In its analysis, the commission also found that the rules are exempt from
Chapter 2007 pursuant to §2007.003(b)(4) because they are reasonably
taken to fulfill an obligation mandated by federal law. The commission has
included elsewhere in this preamble its reasoned justification for adopting
this strategy and has explained why it is a necessary component of the SIP
which is federally mandated. This discussion, as well as the HGA SIP which
is being adopted concurrently, explains in detail that every rule in the HGA
SIP package is necessary and that none of the reductions in those packages
represent more than is necessary to bring the area into attainment with the
NAAQS. This rulemaking therefore meets the requirements of §2007.003(b)(4).
Although the rule revisions do not directly prevent a nuisance or prevent
an immediate threat to life or property, they do prevent a real and substantial
threat to public health and safety and significantly advance the health and
safety purpose and they therefore meet the requirements of §2007.003(b)(13)
as well. For these reasons the rules do not constitute a takings under Chapter
2007 and does not require additional analysis.
BCCA, Entergy, ExxonMobil, Equistar, Goodyear, Lyondell, Phillips 66, REI,
and TPIEC stated that the proposed rules did not include an adequate small
business and micro-business assessment as required under Texas Government
Code, §2006.002. The commenters stated that an analysis of the costs
of compliance for small and micro-businesses must also compare the costs of
compliance for these businesses with the costs for the largest businesses
affected by the rules. The commenters stated that the comparison must use
at least one of the following standards: cost for each employee, cost for
each hour of labor, or cost for each $100 of sales. The commenters asserted
that the rule proposal failed to include the mandated cost comparison standards.
The commenters stated that this is the case even in those instances where
the commission acknowledged a significant impact. The commenters stated that
the commission either restated the costs of compliance it identified in the
analysis of public benefits and costs, or concluded that it cannot determine
the cost to small businesses. The commenters stated that the rule proposal
preamble stated that "the estimated capital and annualized cost of installing
and operating control technology used for the various types of equipment in
fiscal note would appear to be a reasonable cost estimate for small and micro-businesses."
(25 TexReg 8293).
The commenters asserted that the rule proposal's assessments fall short
of what Texas law requires and that it is not sufficient for the agency merely
to state that the costs for small and large businesses will be the same. The
commenters stated that the rationale behind requiring a comparison using an
established standard (e.g., cost for each employee, cost for each hour of
labor, or cost for each $100 of sales) is to determine whether there is a
disparate impact on small businesses. The commenters stated that according
to
Unified Loans v. Pettijohn
, 955 S.W.2d
at 652 (Court of Appeals -- Austin, 1997), the statute's purpose is to obtain
"an objective assessment of the agency's proposed action by forcing it to
consider seriously. . . the effect of the rule on small businesses, including
an analysis of their costs of {compliance} and a comparison of their costs
with the cost of compliance for the largest businesses affected. ..." The
commenters stated further that the commission cannot merely conclude that
the costs to small businesses "cannot be determined," and is obliged to include
in the notice "some basis" for its conclusion so that interested parties can
"confront that basis in a meaningful way in their comments." (
Unified Loans v. Pettijohn
, 955 S.W.2d at 653.)
The commenters stated that in the rule proposal preamble, the commission
did not publish the information mandated by Texas law and that as a result,
it is impossible for the public to comment on whether the agency adequately
considered the effect of the rule on small businesses, thus rendering the
notice of the plan inadequate. The commenters stated that Texas Government
Code, §2006.002, requires the commission to provide a comparison of the
proposed rule's impact on small and large businesses, using the specified
standards, for public review and comment before adoption.
The rules have not been revised based on these comments. The agency has
estimated, to the extent possible, the costs to small businesses and has determined
that there is no cost of the voluntary portion of these rules, Divisions 1
and 4, and that the cost of compliance with the cap and trade program will
be minimal. The only costs created by this rulemaking are the costs of recordkeeping
and reporting. These costs are mitigated for smaller facilities by excluding
those facilities which are ten tons or less. In fact, these rules provide
flexibility for meeting the requirements of the revisions to Chapter 117 regarding
NO
x
reductions from point sources in the HGA
nonattainment area which are adopted concurrent with this rulemaking. To the
extent that the commenters are concerned about the costs of the Chapter 117
rule revisions to small businesses, they may review the response to this comment
in the preamble for those rule revisions which are published elsewhere in
this version of the
Texas Register
.
The comments which state there are critical gaps did not identify what
these gaps are or how that results in inadequate notice. The commission is
unaware of any requests for additional information to which it was not completely
responsive.
BCCA, Entergy, ExxonMobil, Equistar, Goodyear, Lyondell, Peco, Phillips
66, REI, and TPIEC stated that the proposed rules did not include the local
employment impact statement required under Texas Government Code, §2001.022.
The commenters stated that Texas Government Code, §2001.022, requires
the commission to determine whether the rule proposal has the potential to
affect a local economy before proposing the rules for adoption. The commenters
stated that if answered affirmatively, the commission must request that the
Texas Employment Commission to prepare a local employment impact statement
describing in detail the probable effect of the rules on employment in each
geographic area affected by the rules for each year of the first five years
that the rules will be in effect. The commenters further asserted that the
commission failed to make the required initial determination and ignored the
potential for the proposal to adversely affect the local economy. The commenters
stated that a local employment impact statement should have been requested
and prepared in advance of the proposal.
The rules have not been revised based on these comments. The commission
agrees with the commenters that the proposed rulemaking may affect a local
economy, however, does not agree that it is the responsibility of the commission
to provide the local employment impact analysis. The APA requires state agencies
to determine whether a rule may affect a local economy before proposing a
rule for adoption. If the agency determines that a proposed rule may affect
a local economy, the agency must send a copy of the proposed rule and other
information to the Texas Workforce Commission before the agency files notice
of the proposed rule with the secretary of state. The APA requires the Texas
Workforce Commission to prepare a local employment impact statement for proposed
rules, if a state agency requests the statement. The commission determined
that the proposed rulemaking might affect a local economy, and sent the proposed
rules and other requested information to the Texas Workforce Commission. The
commission received a letter from the Texas Workforce Commission, indicating
that the Texas Workforce Commission did not have the ability to determine
the potential local employment impacts from the proposed rules.
BCCA, Entergy, ExxonMobil, Equistar, Goodyear, Lyondell, Peco, Phillips
66, REI, and TPIEC stated that the proposed rules did not include adequate
notice as required under Texas Government Code, §2002.024. The commenters
stated that Texas Government Code, §2001.024, requires adequate notice
of a proposed rule, including information about its public benefits and costs.
The commenters stated that adequate notice is essential for fairness as well
as a meaningful opportunity to comment on a proposed rule, and that courts
have considered notice "adequate" only if: interested persons can confront
the agency's factual suppositions and policy preconceptions; and the agency
provides interested parties the opportunity to challenge the underlying factual
data relied upon by the agency. The commenters asserted that in proposing
the rules, the commission failed to provide interested parties with sufficient
information to constitute adequate notice.
The commenters stated that the rule proposal preamble appears short of
adequate notice because the cost estimates were "dramatically underestimated."
The commenters stated that the commission published insufficient information
and analysis regarding costs and impacts.
The commenters also noted that the rule proposal preamble stated that "there
may be individual sources for which the equipment actual control costs are
higher than the ones identified in this cost note," and asserted that through
this statement the commission "acknowledged that its estimates may have been
low."
The commenters stated that it has identified a number of critical gaps
in the underlying factual data, methodology, and analysis in support of the
proposed rules. The commenters asserted that the proposal included insufficient
information and analysis regarding costs and impacts. The commenters asserted
that the commission has not adequately responded to requests for additional
information from stakeholders. The commenters stated that the following requests
for information were outstanding: information regarding the modeling of emissions;
information regarding the corrected emissions inventory database; and information
supporting the estimated costs of control. The commenters stated that this
information is necessary in order to comment effectively on the proposed rules
and that data gaps in the proposal hindered effective comment.
The commission disagrees with the commenters and has made no change in
response to these comments. Texas Government Code, §2001.024 requires
of the notice of a proposed rule include certain information. Texas Government
Code, §2001.024(5) requires that the notice state the public benefits
expected as a result of the adoption of the proposed rules and the probable
economic cost to persons required to comply with the rule. Adequate notice
is essential for fairness as well as a meaningful opportunity to comment on
a proposed rule.
United Loans, Inc. v. Pettijohn
, 955 S.W.2d 649, 651 (Tex. App.-Austin 1997). To achieve the goal
of encouraging meaningful public participation in the formulation and adoption
of rules by state agencies, the notice must have sufficient information so
that interested persons can determine whether it is necessary for them to
participate in order to protect their legal rights and privileges. The proposed
rules contained an analysis of information available to the commission regarding
the costs and benefits of the proposed rules. Therefore, the commission believes
this goal has been achieved and that the notice includes sufficient information
to constitute adequate notice.
The commission has determined that there is no cost of the voluntary portion
of these rules, Divisions 1 and 4, and that the cost of compliance with the
cap and trade program will be minimal. The only costs created by this rulemaking
are the costs of recordkeeping and reporting. In fact, these rules provide
flexibility for meeting the requirements of the revisions to Chapter 117 regarding
NO
x
reductions from point sources in the HGA
nonattainment area which are adopted concurrent with this rulemaking. To the
extent that the commenters are concerned about the costs of the Chapter 117
rule revisions, they may review the response to this comment in the preamble
for those rule revisions which are published elsewhere in this version of
the
Texas Register
.
The comments which state there are critical gaps did not identify what
those gaps are or how that results in inadequate notice. The commission is
unaware of any requests for additional information to which it was not completely
responsive.
Sierra-Houston and one individual commented that the proposed rules should
be adopted statewide. Others generally comment that the commission should
be doing more than what is proposed in this rulemaking.
The rules have not been revised based on these comments. The commission
appreciates the commenters' support for statewide applicability of the rules.
The commission notes, however, that it is not obligated to adopt all rules
statewide in order to satisfy its commitments under the SIP, nor is the commission
required to do so under the Federal Clean Air Act. Three of the proposed measures
contain emission reduction strategies that have been proposed for statewide
applicability: California Large-Spark Ignition Engines; Emissions Banking
and Trading Program (that portion of the proposed rule which relates to the
trading of emission reduction credits and discrete emission reduction credits);
and Cleaner Diesel Fuel (that portion of the proposed rule which relates to
on- highway fuel).
In evaluating whether to implement all of the rules statewide, the commission
took into account many concerns, including, but not limited to, the need for
the marketplace to be able to respond to regulation, the possible impacts
on transport and distribution systems, the possibility of increased costs
and financial burdens on regulated entities, and regional needs and issues
associated with statewide mandates. The commission analyzed where emission
reduction measures are most needed and where emission reduction measures will
be most effective in order to demonstrate attainment.
An individual stated that the SIP should require reductions in the range
of 90% of VOC and NO
x
for all of East Texas.
The rules have not been revised in response to this comment. The commission
has not determined that reductions of this magnitude are required in East
Texas in order for the HGA area to attain the ozone standard. The cap and
trade program will only affect the HGA eight-county nonattainment area and
will only be used to limit NO
x
emissions. The
commission may investigate the validity of expanding the cap and trade program
to other counties, including East Texas. The commission may also consider
expanding the program to cap other criteria pollutants. If it is determined
that additional counties and/or pollutants should be controlled under the
cap and trade program, further rule making would be required.
One individual commented that these rules are being set up to embarrass
Texas and the Governor, and that he hopes that State Legislators and Congress
would investigate these plans.
The rules have not been revised based on this comment. The commission's
intent is not to embarrass Texas and the Governor, but instead to comply with
the timelines provided in 1990 FCAA amendments and subsequent EPA guidance
for submitting rules to demonstrate ozone attainment in HGA. Accordingly,
Texas has committed to adopting the majority of the necessary rules for the
HGA attainment demonstration by December 31, 2000.
Sierra-Houston resubmitted comment letters dated August 2, 1999, January
31, 2000, and February 24, 2000 concerning already-completed rulemakings and
SIP revisions which Sierra-Houston had initially submitted during the comment
period for these previous rulemakings and SIP revisions.
The rules have not been revised based on this comment. These comments were
addressed in the ANALYSIS OF TESTIMONY section of the preambles to the earlier
rulemakings and SIP revisions which were published in previous issues of the
The EPA commented that authorizations under Chapters 106 and 116 should
be approved as SIP revisions before limits under these Chapters can be used
in the setting of allowances.
The rules have not been revised based on this comment. The commission does
not believe that it is necessary to submit authorizations under Chapters 106
and 116 as SIP revisions. On August 13, 1982, (47 Federal Register 35183),
the EPA published its approval of several revisions to 30 TAC Chapter 116
that were submitted to the EPA for SIP approval on May 9, 1975. Part of that
May 9, 1975 submittal included §116.6, Exemptions. Although §116.6
has since been revised, the version that existed at the time of the August
13, 1982 SIP approval has not been withdrawn from the SIP. Thus, the basic
regulatory authority for exemptions, now permits by rule, is in the SIP. In
a letter dated June 4, 1990 from Merrit Nicewander, Chief, New Source Review
Section, EPA Region VI, to Lawrence Pewitt, Director of the Texas Air Control
Board (TACB) Permits Division, the EPA stated that where the TACB issues standard
exemptions pursuant to state regulations that were developed in accordance
with the Texas SIP, the standard exemptions themselves are federally enforceable.
Additionally, since Chapter 116 itself has been submitted and approved as
part of the SIP, authorizations made under 116 are enforceable by the EPA.
Thus, since permits and permits by rule are federally enforceable, there
is no need to submit each authorization individually as a SIP revision.
Under the definition of "source" the executive director has the authority
to determine whether multiple processes exhausting from single point is treated
as a single or multiple source. The EPA stated the commission should address
how this definition is consistent with new source review and prevention of
significant deterioration requirements.
The commission has made no changes in response to this comment. The definition
of "Source" in both §101.300 and §101.370 are consistent with §101.1
which states that a source is a "point of origin of air contaminants, whether
privately or publicly owed or operated." The definition in these sections
goes on further to state "Upon request of a source owner, the executive director
shall determine whether multiple processes emitting air contaminants from
a single point of emission will be treated as a single source or as multiple
sources." The definition is accurate for its intended purpose for defining
a source of emissions when determining the generation and use of emission
credits under Subchapter H, Divisions 1 and 4. For NSR and PSD purposes, if
a permit were to rely on an emission reduction or emission credit then that
reduction or credit would be applied to the applicable "source" as described
under the NSR or PSD rules and regulations. Since the definition in these
sections applies only to these sections, it does not have to be identical
to the definitions in NSR and PSD programs.
The EPA commented that the rule should address environmental justice issues
for VOC trades such as specific notice of trades to nearby communities. Sierra-Houston
commented that cap and trade programs are not set up to account for environmental
justice issues.
The rules have not been revised based on these comments. Sections 101.302(e)
and 101.372(f) of the adopted rules provide for the executive director to
halt trading for a certain area if problems result from trading in a localized
area of concern. Under §101.373(f)(6)(A), increases in emissions by use
of credits are allowed only on a temporary basis, not perpetually, and are
limited to 25 tons for NO
x
and five tons for
VOC in any 12-month period. Additionally, the only time credits may be used
to increase emissions, the conditions of 30 TAC §106.261(3) or (4) or §106.262(3)
must be met without a specific impacts review, pursuant to §101.373(f)(7).
All other uses would allow sources only to remain at the current emission
rates or lower. Therefore, the commission believes that notice for each trade
is unnecessary and furthermore would significantly hinder the trading procedures
and would discourage use of the trading program.
The EPA commented that it is concerned about creating replicable procedures
for the substitution of VOC for NO
x
reductions
and stated that if the commission's final rules contained such a provision
the determination of VOC substitutions would need the EPA approval.
The commission agrees that interpollutant trading should be approved by
both the executive director and the EPA. The rules have been changed accordingly
in §§101.302(a), 101.356(f), and 101.372(a).
The EPA commented that in the absence of an outlined procedure for demonstrating
an improvement in air quality in the "county of use" of a credit, the EPA
approval would be required for each trade.
The commission agrees that trading between different nonattainment areas
or between attainment and nonattainment areas should be approved by both the
executive director and the EPA. The rules have been changed accordingly in §101.302(e)
and §101.372(e)(5).
The EPA requested confirmation that the provision in §101.303(a) requiring
the EPA approval for deviation from the EPA protocol would limit the clause
"or other model as applicable" in the definition of mobile baseline activity.
No change has been made to the rules in response to this comment. The commission
confirms that §101.303(a) requires the EPA approval of the use of any
mobile model in determining mobile baseline activity. The clause "or other
model as applicable" was meant to incorporate the possibility of models which
may be created and approved in the future without having to identify them
at the present.
The EPA commented that §101.303(e)(3)(I) references regulatory requirements
and should also reference statutory requirements.
The rules were revised to incorporate this comment.
The EPA commented that there appears to be a typographical error in §301.303(e)(4)(I)
and should read...... that is not prohibited.
The rules were revised to incorporate this comment.
The EPA commented that, if an agreed order is used to make a reduction
enforceable, the agreed order should be submitted to the EPA and approved
as a SIP revision before the credits are valid for trading.
The rules have not been revised based on this comment. The commission believes
that agreed orders which are entered by the commission are enforceable by
the EPA through the Texas Clean Air Act which is part of the SIP and through
the specific provision for making reductions enforceable through agreed order
in this rule and therefore do not need to be submitted individually as SIP
revisions.
An individual commented the rules go far beyond what is necessary to protect
the environment. Another individual said the banking rules are illegal.
The rules were not revised in response to these comments. The cap and trade
portion of the banking rules are a method of compliance with NO
x
emission limits that have been demonstrated as necessary to bring
the HGA area into attainment with the ozone standard. The commission acknowledges
that the limits on growth are strict but disagrees that they go beyond what
is required to attain the federal ozone standard. The commission believes
the banking and trading rules are consistent with its statutory authority
to develop a plan for control of the state's air and its authority to issue
permits. Banking and other economic incentive programs are also authorized
for use in the SIP by the FCAA, §110(a)(2).
An individual commented that leak reduction at refineries would remove
the need for strict rules on the public.
The rules were not revised in response to this comment. The commission
requires leak detection as a condition of issuing permits for refineries.
Generally leaks at refineries cause the release of volatile organic compounds.
The principal focus of these adopted rules is a reduction in NO
x
, which is generally emitted due to combustion. The commission believes
that actions are required to reduce NO
x
from
both stationary and mobile sources in order to achieve attainment with federal
air quality standards.
An individual stated that trading makes emission limits more difficult
to enforce and allows emissions to be hidden.
The rules were not revised in response to this comment. The commission
disagrees with this comment. The commission will have a system of tracking
and accounting for allowances at individual sources and therefore will know
what a sources authorized emission limits are at any time similar to the enforcement
methodology of permit allowables. The cap and trade system will not introduce
any new difficulties in enforcing those limits.
An individual stated that the trading program should be supported by continuous
emission monitoring. Periodic monitoring should not be allowed.
The rules were not revised in response to this comment. The commission
believes that it is unrealistic to require all facilities involved with emissions
trading to have continuous monitors installed. The cost and need for this
requirement is undocumented. If continuous monitoring data is available, it
will be used to calculate actual emission reductions. If continuous monitoring
is not available, the commission will utilize the best replicable data available,
including periodic monitoring, stack sampling, and mass balance calculations.
The monitoring requirements for each category of facility is generally set
by the rules which apply specifically to those facilities, not by the banking
rules. In this way the commission has been able to consider whether the cost
of continuous monitoring is outweighed by the benefits for each category of
facility.
Two individuals suggested a moratorium on permits.
The rules were not revised in response to this comment. The cap and trade
program is designed to cap emissions of NO
x
at
a level determined to result in attainment of the ozone air quality standard.
Because emissions will be capped, no significant increase in overall emissions
can occur from permitting activity thus a moratorium on permits is unnecessary.
BCCA, LCR, and Chevron commented that the commission should establish emission
trading programs for federally preempted mobile and non-road sources. Such
a program should allow for the trading among source categories. HGAC, RAQCG,
and The Council commented that certain mobile source emission control programs
such as Diesel Emulsion, Accelerated Purchase of Tier II/III Diesel, and NO
The rules were not revised based on these comments. The rules will allow
any source, including stationary, mobile on-road, and mobile off-road, to
bank reductions that are beyond local, state, and federal rules and regulations,
provided that the requirements of Chapter 101, Subchapter H, Divisions 1 and
4 are met. To the extent that the control strategies mentioned by the commenters
are not already required of the source, they could potentially be creditable.
HGAC commented that the commission should better define what emission reductions
are available outside the proposed controls so generators have a greater certainty
that they can enter into legitimate trades.
No changes have been made in response to this comment. The rules allow
for any reduction that goes beyond any mandatory state or federal requirement
to be banked as a credit so long as the reduction meets the requirements of
30 TAC Chapter 101, Subchapter H. Each individual source will have to review
its own processes to determine the potential for reduction which can be banked.
LWV-TX commented that any emissions banking and trading program should
result in reductions within the same airshed.
No changes have been made in response to this comment. The banking and
trading program is designed to reduce NO
x
within,
and is currently limited to, the eight-county HGA area. The program does not
allow for the trading of allowances (emissions) into the area from outside
the designated eight counties. Additionally, the ERC and DERC trading programs
allow only credits created within a nonattainment area to be used within that
same nonattainment area until such time as a demonstration can be made that
there is an equivalent air quality benefit to trading between these areas.
Sierra-Houston opposed trading of credits between nonattainment areas and
the trading of credits generated in the county, state, or nation. They preferred
the actual reduction of emissions.
No changes have been made in response to this comment. The commission only
supports trading of credits between counties, states, or nations if it does
not adversely affect air quality for any given area. Such a demonstration
would require approval of the executive director and the EPA. Trading provides
an incentive to reduce emissions since reductions result in an allowance saving
that has market value.
Sierra-Houston opposed the trading of one contaminant for another and allowing
the executive director discretion in determining the amount of allowances
allocated to a source. They stated these provisions of the rules would not
result in real reductions.
The commission has not changed the rules in response to this comment. The
commission disagrees that trading will not result in real reductions. To the
extent that it enables the commission to achieve more overall reduction through
other rules, the trading program provides a benefit to air quality. Additionally,
trading of ERCs and DERCs in many cases requires the retirement of 10% of
the credits used to benefit air quality.
The commission will allow the trading of one contaminant for another if
it is demonstrated that an equal environmental benefit is accomplished. For
example, if it is sufficiently demonstrated that a reduction of ten tons of
VOC would reduce ozone formation in the same way as a reduction of one ton
of NO
x
, the rule would allow for interpollutant
trading at a ratio of ten to one. This demonstration can only occur if a real
reduction is made and must be approved by the executive director and the ED.
Given the continuing development of the science of ozone and the fact that
both VOC and NO
x
are precursors to the formation
of ozone, it is possible that this flexibility will provide a mechanism to
better reduce ozone in nonattainment areas.
Regarding the executive director's discretion to deviate from the standard
allocation for allowances, the executive director plans to detail the factors
which may be considered for deviation from allocation methodology in a guidance
document. The executive director plans to limit deviations to extraordinary
circumstances, for example a catastrophe which required a facility to shut
down during the historic period upon which allocations would normally be based.
The intent of this provision is to prevent significantly low allocations due
to the fact that the historic period is not representative a plant's emissions.
SNTG commented that creditable reductions from mobile sources be calculated
between the low emitting technology used and the lower of the conventional
emission rate and the most stringent allowable emission rate.
There has been no change to the rules in response to this comment. The
commission believes that the rules as adopted already accomplish the goal
of the commenter. The definition of "surplus" allows only reductions beyond
existing requirements to be creditable. So in the event that there is an allowable
emission rate which is more stringent than the conventional emission rate,
that allowable emission rate would determine how much of the reduction is
surplus and therefore creditable.
SNTG commented that emission credits should be generated by comparing an
emission reduction strategy to emissions that would otherwise occur without
the strategy. This would eliminate the need for a baseline and allow reductions
to be accomplished earlier.
The commission has made no changes in response to this comment. The SIP
requires that the generation of allowances and credits be accomplished through
comparison to a baseline of emissions. Surplus credits can only be generated
when an emission control strategy results in reductions not required by any
rule, regulation, or order.
TIP, Texas Eastern, TxOGA, Valero, and REI commented that the term baseline
emissions should be defined as a source's actual emissions averaged over any
consecutive 24-month period between the beginning of the SIP year and the
emission reduction strategy period. Fixing the emission baseline to the SIP
year is arbitrary and capricious. Where 24 months of data is not available,
the executive director may consider any consecutive 12-month period. The definition
of baseline activity should be similarly constructed based on operating hours,
production rates, types of material processed or combusted. They also commented
that the adopted rule should contain a definition of SIP Year as the year
of emission inventory data on which applicable SIP provisions are based.
The rule has not been revised based on these comments. The trading programs
were developed to provide flexibility to facilities that choose to purchase
emission credits in lieu of making actual reductions that would otherwise
be needed as part of an attainment strategy. By allowing facilities to use
higher baseline emissions, the total number of credits generated from an emission
reduction would exceed the facility's emissions as listed in the baseline
year which was relied upon for planning purposes of the SIP strategy. Under
the commenters' recommendation, double counting of emission reductions in
the SIP would be possible. The commission must link the baseline to the SIP
year in order to have a stable point from which to plan and therefore the
requirement is not arbitrary and capricious.
TIP, TxOGA, Valero, and REI commented that the requirement for an emission
reduction to have occurred after the most recent year of emission inventory
used for SIP determination in order to be creditable lacks reasoned justification.
The timing of reductions should not be limited in this manner.
No change was made in response to this comment. The commission believes
that any reduction that occurs prior to a year in which the emissions inventory
was relied upon for a SIP demonstration should not be creditable because that
reduction, unless already in the bank, will have been relied upon as part
of the emission inventory. It would be considered "double counting" if the
same reduction were relied upon for SIP purposes and also banked as a credit
which could be relied upon to add emissions back to the atmosphere.
HGAC commented that the commission should reconsider allowing trades of
VOC and particulate matter (PM) across source types as these contaminant categories
contain several toxic elements.
No change was made in response to this comment. There are restrictions
on use of VOC discrete credits in §101.373(f)(7) to protect against the
potential impact of different types of VOC and PM. Facilities trading PM or
VOCs may be subject to a health effects review for any increase in emissions.
Any review would be conducted independently of the trade and can result in
a restriction on the use of credits regardless of the amount of credits transferred
during the trade. Owners of facilities trading PM or VOCs should be aware
that this restriction may be applied upon use thus reducing the value of their
trade.
TIP, TxOGA, Valero, and REI commented that the Protocols section of the
proposal is confusing and that the subjects of the section, credit generation,
calculation, registration, and certification should be moved to their own
sections. SNTG commented that the rule should be subdivided into divisions
for ERCs, MERCs, DERCs, and MDERCs for clarity in terminology.
The rules were not revised in response to these comments. This adoption
is the first step of consolidation and reorganization of emission banking
and trading rules into one subchapter. The commission agrees that there is
a need for further refinement and reorganization and intends to address these
issues in future rulemaking.
TIP, REI, TxOGA, Valero, and PIAT commented that the usable life of ERCs
should remain at 120 months and the proposal lacks reasoned justification
for the reduction in usable life to 60 months.
No changes have been made in response to this comment. The commission has
chosen to limit the life of ERCs registered after the effective date of this
rulemaking to 60 months from the date the reduction occurred. This change
is made to reduce the effect of older reductions on future SIP strategies.
The commission has received comments in the past regarding the use of credits
for new projects which were five to ten years old. Based on this public concern
and the concept that credits generated ten years ago are too remote to allow
resurrection of the emissions, the commission has reduced the life of unused
ERCs to five years. ERCs registered prior to the effective date of this rulemaking
will continue in effect for 120 months.
TIP, TxOGA, Valero, and REI commented that there is no reasoned justification
for the requirement to register reductions within 180 days of generation.
Such registration should be annual. They further commented that the rule should
be clear that failure to register only prevents a source from taking credit
for its reduction and is not a matter for enforcement.
The commission has not revised the rule in response to these comments.
The commission believes that it is crucial for SIP planning purposes to know
which reductions will be banked and thus relied upon in the future for emission
growth and which reduction can be relied upon as a permanent reduction. By
requiring a project to be registered within 180 days of the reduction, the
commission will be able to accurately make that decision. It is possible for
air quality strategies to be developed from concept to adopted rule in a six-month
period therefore the commission believes the 180 days is needed to provide
adequate information on the potential emission reduction credits which could
effect the decision making for that strategy. Since participation in the banking
program is voluntary, the commission agrees that it should not be an enforcement
issue if the 180-day deadline is missed; it simply means the generator has
lost the opportunity to bank that reduction as a credit.
One individual stated that there should be no pooled reductions. PIAT requested
the option to combine credits into larger blocks for sale to larger companies.
No changes have been made in response to these comments. Credits may be
sold individually or in blocks, however, ERCs may not be grouped together
and treated as a unit unless the reductions occurred on the same day since
ERCs expire based on the generation date.
TIP, TxOGA, Valero, and REI commented that the proposal requires the EPA
approval of deviations from emission credit protocols. There is no reasoned
justification for this requirement given the commission's responsibility for
administering the program.
No change was made in response to this comment. The EPA has established
or approved state protocols for emissions trading programs, and, under their
guidance document, deviations from those protocols must be EPA approved. Since
this banking program is part of the state SIP the commission believes that
it is prudent to require the EPA approval to ensure that the program will
remain viable under the SIP.
Spring Valley commented that the commission should establish an offset
ratio for mobile source emission reduction credits because the generation
of mobile emission credits is cheaper than credit generation at stationary
sources. RAQCG commented that the commission should consider making the mobile
source credit program a separate economic incentive program.
The rules were not revised in response to these comments. The commission
believes that establishing an offset ratio for mobile credits would reduce
the incentive to develop mobile source control programs and technology and
chooses not to implement an offset ratio. If the commenter is correct that
mobile emission credits are cheaper to generate the commission expects the
market to generate enough incentive to bring about those reductions to be
used by point sources. The commission desires to provide maximum flexibility
within the cap and trade program and promote mobile source control programs.
Therefore the commission will allow unlimited use of MDERCs by sources under
the cap and trade program.
TIP, TxOGA, Valero, and REI commented that the proposal prohibits ERC generation
from emission reductions resulting from transferring emissions to another
piece of equipment. As drafted, the proposal is ambiguous and may interfere
with the use of reductions in netting or offsets. They recommend that the
definition of "real reduction" be modified so that a transfer of emissions
to another unit would be considered a real reduction if it is used in offsetting
under §116.150, New Major Source or Major Modification in Ozone Nonattainment
Area.
No changes have been made in response to these comments. The rules as proposed
allow internal reductions to appear within a netting window but do not allow
transferred reductions to be creditable as banked emission reductions. Further
clarification will be available through technical guidance after adoption
of the rules.
TIP, TxOGA, Valero, and REI commented that the rule should make clear that
reductions resulting from the application of state reviewed best available
control technology are surplus.
No changes have been made in response to this comment. The commission understands
the commenters' concern and the commission will continue to review this issue
to determine if best available control technology is relied upon for the SIP
and should not be creditable. If a rule change is determined to be necessary
it will be proposed in the future.
TIP, TxOGA, Valero, and REI commented that the enforce ability of ERCs
following registration using the OPCRE-1 Form should not be limited to grandfathered
sources or those sources that use a permit by rule.
No changes have been made in response to this comment. The commission believes
that the enforceable mechanism for a permitted facility should be a modification
to that facility's permit. The OPCRE-1 Form is strictly used as an alternative
to obtaining an agreed board order for grandfathered sources. Sources authorized
under permits by rule have always been restricted to using the PI-8 Form.
The EPA commented that the equation in §101.303(f)(8) does not contain
variables for a nonattainment area offset ratio or the 10% environmental benefit.
The equation should match the rule text.
No change has been made to the rules in response to this comment. The equation
in §101.303(f)(8)(C) applies to the limited circumstances where credits
are used to exceed a source cap under Chapter 117. In those instances the
nonattainment area offset ratio and the 10% environmental benefit do not apply.
The text in §101.303(f)(8)(A), (B), and (D) apply to other types of credit
uses and specifies what the offset ratio and environmental benefit should
be.
Peco commented that the equation in §101.303(f)(8)(C) divides credit
into 365-daily increments. This eliminates most credit for units that operate
a few weeks or days per year. They also commented that electric generating
facilities constructed after January 1, 1999 should be able to use authorized
daily heat input as specified by §117.210(c)(1) to determine activity.
The equation that Peco refers to is not applicable to Peco's proposed new
facility located in HGA. The equation was developed for use in emission reduction
credit trading for sources operating under the source cap, §117.223.
The source cap of §117.223 is a voluntary compliance mechanism for industrial,
commercial and institutional (ICI) facilities complying with NO
x
RACT in BPA, DFW, or HGA, or the attainment demonstration emission
specifications for ICI facilities in DFW or BPA. The system caps in §117.108
and §117.210 are compliance mechanisms for EGFs complying with the emission
specifications for the attainment demonstration in BPA, DFW and HGA. Participation
in these caps for EGFs are voluntary in BPA and DFW, and mandatory in HGA.
The commission did not propose a procedure for system cap emission trading
for EGFs in HGA in the August, 2000 proposal to these adopted rules. However,
a system cap emission trading rule for EGFs in DFW was proposed in the December
1, 2000 issue of the
Texas Register
(25 TexReg
11886). Final action will be taken on this rule proposal by May 31, 2001.
In a future rulemaking, the commission may develop system cap trading rules
for EGFs in HGA.
Cap and Trade Comments
TXI commented that the program lacked flexibility.
The commission has made no changes in response to this comment. The commission
believes that it has provided considerable flexibility within the framework
of a stringent cap on NO
x
emissions. This flexibility
is accomplished through the unrestricted trading of allowances and the ability
to use DERCs and MDERCs within the cap. This is an alternative to enforcing
emission standards on a facility-by-facility basis which provides the facility
operators significant flexibility.
TxOGA and Valero requested the adopted rule contain a statement that allowances
and trades are not applicable requirements under Federal Clean Air Act Title
V (Title V) requirements.
The commission has made no changes in response to this comment. The cap
and trade program is submitted as a revision to the SIP and, as such, the
restrictions under this program are applicable requirements under Title V.
TIP, TxOGA, Valero, Peco, REI and BCCA objected to the daily and monthly
NO
x
limits for utility sources in addition to
the annual cap. These limits render the cap and trade flexibility meaningless.
The commission disagrees with this comment and has made no changes to the
rules. The 30-day average system cap emission limit functions as a flexible
but controlling limit which ensures that a specified emission level is achieved
during a typical peak ozone season day. The much less stringent daily maximum
limit ensures that the 30-day average is not manipulated to allow higher NO
Note that the commission has modified the system cap requirements in §117.210
to exclude cogeneration units whose electric output entirely serves one or
several dedicated industrial customers, except when the industrial customers
are not operating. These sources are base load sources and are not operated
at higher levels on hot summer days to meet electric demand and would not
contribute additional emissions during these periods.
The commission disagrees that these daily and monthly limits render the
ability to trade meaningless because trading can still be useful to meet annual
limits. As discussed in a previous response, in a future rulemaking, the commission
may develop system cap trading rules for EGFs in HGA which would enable trades
to occur among companies. This development would enhance the flexibility of
cap and trade compliance.
Sierra-Houston generally opposed the concept of the cap and trade system
and stated that it allows some sources to escape reductions. An individual
commented that the cap and trade program should be limited in duration and
credits should be generated and used only by companies that make actual emission
reductions. Two other individuals added that large companies could buy their
way out of reductions. Four individuals commented that banking and trading
only allows shifting of emissions and that all industries should be required
to reduce. Three individuals stated that trading will leave emissions in the
poorer neighborhoods.
The commission made no changes to the rule in response to these comments.
The cap and trade program is applicable in all eight counties of the HGA area
so that reductions are made throughout the nonattainment area. The underlying
goal of the program, in conjunction with the Chapter 117 limitations on point
source emissions, is to reduce the overall amount of NO
x
emitted from point sources by approximately 90%. This reduction of
NO
x
will then reduce the formation of ozone in
the area. The reductions of NO
x
and the formation
of ozone are not localized problems in the way that VOCs can be. NO
x
itself does not have a health impact on nearby neighborhoods. The
reductions of NO
x
emissions will benefit the
nonattainment area as a whole by reducing the amount of ozone formed in the
atmosphere.
The cap and trade program is designed to give owners the option of making
reductions or purchasing additional allowances. If allowances are for sale,
that means the holder of those allowances did not actually emit the amount
of NO
x
that it had historically. This in turn
means that a facility using allowances in lieu of making real reductions is
able to do so because another facility in the same area has lowered its emissions
by the same amount. Because there will be a finite number of allowances available
the overall emissions in the HGA area, NO
x
will
remain at levels that are necessary to demonstrate attainment of the ozone
standard. As the implementation schedule proceeds, the HGA area will have
fewer allowances available on the market which means that some reductions
are likely to occur at all facilities as emission standards are tightened
and allowances become more expensive.
The commission believes that the flexibility provided by the trading program
provides the commission, in part, the ability to require the level of reductions
required of the point sources in the HGA area.
TIP, Chevron, Dow, Dynegy, Entergy, Enterprise, Equistar, ExxonMobil, Goodyear,
Lyondell, NASA, Peco, Phillips 66, REI, Texas Eastern, TxOGA, TPIEC, Valero,
and BCCA commented that the proposed NO
x
reductions
that the cap and trade rule are intended to implement are not technologically
or economically feasible and will not result in an economic incentive under
the cap and trade rule because there will be insufficient surplus allowances.
The cap and trade system should be based on current California point source
controls, which are the most stringent achieved in practice. TCC commented
that Emission Specifications for Attainment Demonstrations should be achievable
with proven technology.
The commission made no changes in response to these comments. Point source
NO
x
reductions in the range of 90% require the
combined use of combustion modification and flue gas controls on the majority
of large combustion units. The capabilities of both combustion modifications
and flue gas controls are well documented in the NO
x
control literature, including the EPA ACTs, papers at numerous meetings
of research and trade organizations for industry, NO
x
control vendors, constructors, and the government. These documents
report combustion-based reductions from minimal to over 90%, and flue gas
controls in the range of 75% to 95%. Reduction capabilities as reported in
the literature continue to improve and technology has developed rapidly since
the late 1980s when a number of California districts set retrofit NO
NASA commented that because they have multiple small sources which constitute
a major source, it is unlikely that they will have any emission reductions
to trade. They stated that the program will create uncertainty for future
allowance costs which would create a hardship on an agency that has its budget
decided years in advance. They also expressed concern that the compliance
time frame was unreasonably short, roughly two years, as opposed to the acid
rain or RECLAIM programs.
The rules have been revised to address the concerns of the commenter. NASA
operates a number of gas-fired boilers which are subject to the emission specifications.
These boilers all operate at relatively low capacity factors. The commission
has adopted a less stringent emission standard for low capacity factor units
which operate less than 14 days per year, which will reduce NASA's costs of
compliance. In addition, the compliance schedule has been lengthened, which
will allow NASA at least three years to develop an emission reduction strategy.
The adopted compliance time frame allows the maximum feasible time under the
federal requirement to attain the ozone standard in HGA by 2007.
FPL commented that the extremely low NO
x
emission
limitations simultaneously proposed in Chapter 117 means that very few surplus
allowances will be available on the market. The proposed requirement to obtain
allowances before a new source can operate means that these new sources can
only obtain allowances if an existing source shuts down. The proposal therefore
does not allow for any growth in the HGA area. FPL recommended that the commission
set aside a number of allowances for use by new sources. Enron and Coalition
recommended that allowances be set aside for new sources to bring new and
cleaner sources into the program.
No changes have been made in response to these comments. The commission
believes that sources will be able to generate additional allowances not only
through shutdowns, but also by improving emission control technology. The
commission also believes that allowing the use of discrete emission reduction
credits (DERCs) and mobile discrete emission reduction credits (MDERCs) will
allow stationary sources to find flexibility for growth from NO
x
sources not subject to the cap and trade program. The commission
agrees that the intent of the rule is to stop growth of emissions, but disagrees
that the rule will stop economic growth. With cleaner technology always being
developed, the commission anticipates that point sources will be able to grow
while keeping their emissions low. The commission disagrees that allowances
should be set aside for growth as this would create a first come first serve
scenario putting undue pressure on staff to determine who should receive allowances
first and it could give new facilities sources a significant benefit at the
expense of existing entities.
CAAC commented that cap and trade systems have fallen short of anticipated
environmental benefits and that the commission should continue with the trading
system currently in operation. They also recommend that the commission adopt
third party verification of emission credits as opposed to executive director
approval which could cause delays in approval.
The rules were not revised in response to these comments. The cap on NO
CAAC commented that the cap and trade system will encourage purchase of
power generated from higher emitting sources outside the area of the program.
They also stated that the allocation of allowances is not necessary and credits
should only be generated when a source remains below its established cap.
The rules were not revised in response to these comments. The cap and trade
program does not prohibit the purchase of power outside the affected area
of cap and trade. This will be a business decision of the buyer and will depend
on their cost of reducing emissions, allowance availability and cost, and
availability of power outside the HGA area. Allowances provide a convenient,
flexible, and timely method for facility operators and the commission to track
a facility's status in relation to its emission cap.
An individual opposed the cap and trade program based on the argument that
it strengthens an argument that there is a right to pollute and that it allows
sources to avoid reducing their emissions. The individual supports the command
and control method of achieving reductions.
The rules were not revised in response to this comment. The permit system
is based on the concept that owners of facilities obtain an authorization
to emit contaminants. The preamble clearly states that permits and authorizations
are not property rights and are therefore not protected as such under the
law. The cap and trade program will not eliminate the need for prior authorization
to construct and operate significant sources of air contaminants nor for rules
which could be considered command and control strategies.
TIP, Chevron, Dow, Dynegy, Entergy, Equistar, ExxonMobil, GPA, Kinder Morgan,
Lyondell, Peco, Phillips 66, REI, TxOGA, TPIEC, TGC, Valero, and BCCA stated
that the requirement to trade allowances in whole tons lacks reasoned justification.
The number of allowances is rounded up or down whichever provides the holder
or buyer less credit. Some credits have been traded with a value of $80,000
per ton and rounding can result in the taking of considerable value. They
recommend that trading occur in one-tenth tons. This is consistent with ERC
trading. Texas Eastern also recommended allowances be traded in tenths of
a ton. TGP recommended that fractions of allowances be rounded up rather than
down. During the years of target allowances, rounding down can result in zero
allowances.
The commission has modified §101.350(1) to divide allowances into
tenths of a ton. The commission agrees that there is a potential for the need
to trade and use allowances in smaller quantities than whole tons thus the
rule has been revised to state that allowances will be allocated, transferred,
or used in tenths of a ton. The rounding methodology was not changed from
the normal mathematical rounding procedures however, by allocating, transferring,
and using allowances in tenths of tons will reduce the impact of rounding.
An individual commented that the cap should be limited to the central urban
county (Harris).
The rules were not revised in response to this comment. The modeled attainment
demonstration conducted by the commission indicates that reductions are required
over a wider geographic area other than Harris County in order for the Houston/Galveston
to attain the ozone standard. As discussed in the background of the preamble
to this rule, scientific study has clearly demonstrated that ozone is more
of a regional problem than a local one. Emissions from the surrounding seven-
nonattainment counties contribute to the ozone formation within Harris county
and must be reduced significantly in order for the entire eight-county nonattainment
area to demonstrate attainment with the ozone standard. Applying the cap and
trade program to the entire eight-county nonattainment area ensures that there
is not an excess of allowances available for trade back into the central county.
Enron commented that the cap and trade program should be expanded to areas
out of the eight-county Houston/Galveston nonattainment area to promote a
high volume of allowance transactions. Kinder Morgan and Pasedena recommended
including minor sources in the trading program.
The rules have not been revised based on these comments. The intent of
this program is to cap emissions in the HGA area at existing levels. The commission
has not yet determined that this restriction is necessary outside of the HGA
area. The commission may determine at a later date that including surrounding
counties into the cap and trade program would benefit the air quality and
help the HGA area reach attainment. The cap and trade program will include
minor facilities, with standards under Chapter 117, down to a design capacity
of ten tons of NO
x
per year. The commission intends
to revise the cap and trade rules to include minor facilities at sites that
collectively have a design capacity of ten tons per year or more.
BASF commented that the ten tons per year (tpy) applicability threshold
for the cap and trade system should apply to accounts or sites rather than
individual sources. Because sources under ten tpy would not receive allowances
they would be required to meet NO
x
emission limits
through cost- ineffective controls. They suggest replacing the term "source"
in §101.351 with the term "NO
x
cap account."
TIP, Chevron, Dow, Dynegy, Entergy, Equistar, Peco, Phillips 66, and BCCA
commented that the term "source" is used to denote an overall site over the
ten-ton applicability trigger but is also used to denote a single emitting
unit. TIP, BCCA, Chevron, Dow, Dynegy, Entergy, Equistar, ExxonMobil, Lyondell,
Phillips 66, REI, Solutia, Texas Eastern, TxOGA, TPIEC, Valero, and BASF commented
that sources not subject to emission specification for attainment demonstration
(ESAD) rates under the SIP that can make cost effective reductions should
have the option to participate in the cap and trade program and its allowances
allocated in the same manner for current ESAD sources.
The rules have not been revised based on these comments. The commission
had intended the cap and trade program to apply to all facilities at sites
that have emission specifications under Chapter 117 and collectively have
a design capacity of ten tons or more of NO
x
emissions per year. However, due to the use of the term source in the proposal,
that intent was not clear from the rule language. In order to ensure that
all potentially impact entities have the opportunity to comment on their inclusion,
the commission intends to propose a revision to the cap and trade rule in
the near future which would clarify that the applicability of the cap and
trade program is determined by the collective emissions at a site and that
the ten-ton per year applicability requirement does not apply to individual
facilities. Facilities not subject to the cap and trade program will be able
to generate DERCS which are allowed to be used along with allowances under
the cap and trade system. They will also be able to create and to use ERC
under the existing banking program.
Dynegy and RMT recommended replacing the term "design capacity to emit"
in §101.351 with "potential to emit." as the terms appear to be identical.
Calpine commented that the commission should define the term "design capacity
to emit." It is not clear if emissions are pre- or post-control.
There were no changes to the rules in response to these comments. The term
"design capacity to emit" refers to the capabilities of particular equipment
regardless of enforceable limitations. The term "potential to emit" is a term
of art which is commonly used in reference to the Title V operating permits
program and means the capability to release air contaminants as limited by
pollution control equipment and authorized levels of release. Since there
are specific nuances of the term "potential to emit" that do not apply to
this program, such as synthetic minors, the commission is not using this term.
TIP, Chevron, Dow, Dynegy, Entergy, Equistar, ExxonMobil, Lyondell, Peco,
Phillips 66, REI, TxOGA, TPIEC, Valero, and BCCA believe that one month is
an inadequate period to calculate a control period's emissions and compare
those emissions to cap and trade activity for the control period to balance
the account. They recommend April 1 of the succeeding year as the deadline
for reconciling accounts. Calpine and RMT recommended a one month extension
to March 1. Calpine and RMT also commented that the deadline of March 31 for
submitting compliance reports is too short as CEMS data must be manually quality
controlled. They suggest a one month extension.
No changes have been made in response to this comment. It is the commission's
intent that facilities should actually have the allowances in their compliance
account to cover emissions prior to their actual withdrawal. It is not the
commission's intent to allow facilities to emit and then try to obtain allowances
after the fact. Although this is not prohibited under the rules, it is discouraged
by the limitation of the true-up period to one-month. As proposed, the rules
are on the conservative side and will allow facilities a 30-day grace period
to obtain allowances to balance emissions. In addition, the final reporting
deadline has not been revised and currently parallels the commission's emission
inventory reporting guidelines.
TIP, Chevron, REI, TCC, TxOGA, and BCCA commented that the rule should
be modified to allow compliance with an emission cap to satisfy both nonattainment
new source review and prevention of significant deterioration.
No changes have been made in response to this comment. The commission agrees
that the cap is being permanently set at a level for stationary facilities
for the HGA area to reach attainment. The commission believes that if all
stationary facilities operate under the cap that performing netting and requiring
offsets for new or modified facilities may not be necessary to attain and
maintain the federal air quality standard. However, because these are specific
federal statutory requirements, removing the netting and offset mandates would
require amendments to the Federal Clean Air Act. The commission also believes
that any facility having major increases of NO
x
should undergo a nonattainment/prevention of significant deterioration review
to ensure they are meeting BACT or LAER as applicable, regardless of whether
the facility operates under the cap.
Calpine and RMT requested clarification or an example where an allowance
could be simultaneously used to satisfy an offset requirement as well as used
for cap and trade purposes.
The rules were revised based on this comment to clarify the language in §101.352(e).
Compliance with the cap and trade program requires industry to retire one
allowance for every ton of NO
x
emitted. Offset
requirements are under a separate program and require in the HGA nonattainment
area 1.3 tons of NO
x
credits to be retired for
every ton of NO
x
proposed to be emitted from
a new major source or modification in the HGA area. Under these adopted rules,
in §101.352(e), and under proposed changes to Chapter 106 as published
in the October 20, 2000 issue of the
Texas Register
(25 TexReg 10445) and Chapter 116 as published in the October 20,
2000 issue of the
Texas Register
(25 TexReg
10449), compliance with the NO
x
cap and trade
program (retiring one allowances for every ton of actual NO
x
emissions) may be used for the one-to-one portion of the NO
For example, if a new major facility was constructed in the HGA nonattainment
area which would emit 100 tons per year of NO
x
,
the source would have to satisfy the cap and trade requirements by obtaining
100 tons of allowances. Those allowances could also count toward the facility's
offset requirement so that only 30 tons of NO
x
DERCs, MDERCs, ERCs or MERCs would be needed to satisfy offset requirements
for NO
x
.
The EPA commented that any baseline for determining allowances should be
adjusted downward for any state and federal laws enacted since the last emission
inventory used for an attainment demonstration.
The commission has included language in the provision regarding initial
allocations, as listed in variable (3) of Figure §101.353(a) to ensure
that allowances will not exceed existing federal or state regulations, rules,
or permit allowables.
Avista-Steag commented that portions of the allowance calculations for
2003 and 2004 are ambiguous and subject to differing interpretations and requests
that the commission provide additional and adequate public notice so that
affected parties can determine the effect of the rules and comment meaningfully.
TIP and BASF commented that the calculations to achieve equal third reductions
must be revised. FPL and LCR commented that the equations reducing a source's
allowances do not result in equal third reductions and should be revised.
Calpine and RMT commented that the equations did not result in equal third
reductions and the wording of the calculation methodology is unclear.
The commission has revised the rule to remove the ambiguity concerning
allowance calculations, however, the commission did state in the preamble
the clear intent to reduce allowances by a third of the difference between
the initial allocation for 2002 and the calculated final allocation for 2005.
The commission believes this statement served its intended purpose of soliciting
comments on the allocation concept and the need for clarification to the rule
language is not sufficient cause for re- notification. The equation in §101.353
has been revised to require all boilers, auxiliary steam boilers and stationary
gas turbines within an electric power generator system, as defined in §117.10
to reduce their emissions by an average 44% beginning March 31, 2003, another
average 44% by March 31, 2004, and another average 5% by March 31, 2007, for
a total of an average 93% overall reductions. All other facilities subject
to the cap will be required to reduce their emissions by an average 40% by
March 31, 2004, another an average 40% by March 31, 2005, and another average
10% by March 31, 2007, for a average total of 90% reductions.
BASF commented that the commission should clarify what method will be used
to determine allowances for a newer source where two years of activity data
is not available.
No changes have been made based on this comment. As stated in the response
to the previous comment, the rules have been clarified, however, the methodology
for new or modified facilities has not changed with the exception of the percentage
reduction requirements. Facilities that are not in the 1997 - 1999 inventories
and that do not have two years of actual data will receive allowances based
on that facility's authorized level as stated in the permit or permit by rule
until such time as it accumulates two years of actual data. This method is
stated in variables (2)(B) and (3)(B) in Figure 30 TAC §101.353(a).
Avista-Steig encourages the commission to adopt an allowance distribution
program based on a source's overall effect on air quality.
No change was made based on this comment. The commission will distribute
allowances based on a facility's emissions as adjusted for the required reductions.
The commission is seeking to accomplish an overall reduction in NO
x
for the HGA area of approximately 90%. The commenter is not clear
whether allocations for larger facilities should be reduced in greater proportion
than a smaller facility because of the larger facility's greater air quality
effect or whether the larger facility should continue to receive more allowances
based on its size and activity level or whether different categories of facilities
should be treated different. Allowances under the cap and trade program are
established under the regional cap for the HGA area. The initial allowances
will be based upon historical data while Chapter 117 will determine the final
allocation amount.
BCCA, Dow, Dynegy, Entergy, Equistar, ExxonMobil, GPA, Kinder Morgan, Lyondell,
Pasedena, Phillips 66, TCC, TPIEC, Valero, and Chevron commented that a consecutive
12-month period would more accurately reflect activity levels and would reduce
requests for case-by-case reviews. Kinder Morgan and TGC recommended an alternative
where the most representative three year period during the span 1995 - 1999
be used to determine activity level. Chevron commented that the baseline for
allocation of allowances should be the six months of highest activity from
1995 to rule promulgation. As an alternative they suggest using an average
level of activity determined during periods when equipment is operating as
a substitute for periods of equipment turnaround or shutdown in the calculation
of allowances. Texas Eastern commented that using an average of three years
activity for baseline calculations does not allow for extended maintenance.
Calpine and RMT commented that using an activity average for two years will
cause a steady loss of allowances due to mechanical outages, economic conditions,
or natural disasters. New sources will also reduce the pool of available allowances.
Eventually sources may have to curtail activity because of scarcity of allowances.
Calpine and RMT recommended that allowances be based on the higher activity
level for the first two years of operation. FPL and TCC commented that basing
allowances on activity level imposes an additional emission restriction over
that contained in Chapter 117 and recommended that allowances be based on
permitted or authorized activity levels. Diamond-Koch also recommended that
allowances be based on potential or authorized activity levels. TGP recommended
using the average of the two highest years of actual activity for 1997, 1998,
and 1999. CPS commented that the commission should establish a baseline of
the highest activity year since 1990 for the determination of allowances.
They suggest 1995 as an alternative because accurate NO
x
data is available as that was the first year that CEMS were required
for acid rain facilities. The EPA commented that §101.353(a)(4) seems
to allow sources to determine the amount of their allowances. The EPA requested
the commission address how the cap will be limited to the emission inventory
of an EPA approved attainment demonstration.
No changes have been made in response to these comments. The commission
has based the SIP strategy on the 1997 emissions inventory. To alleviate restrictions
on any one given facility, for example a facility down for maintenance during
1997, the commission chose to use a three-year average to determine the activity
level. However, if all facilities were allowed to choose either the highest
12-month or three-year activity level, the cap would be based on activity
levels much higher than those used for determining the level of reductions
necessary for the HGA area to reach attainment. The commission has chosen
to use the 1997, 1998, and 1999 because they are the most recent and should
best represent the emissions of facilities currently in operation. As noted
in the rules, the executive director may deviate from using the average from
these three years in extenuating circumstances.
An individual stated that sources should not be allowed to determine their
own activity rate, thus their allowances, and emission inventories are not
a reliable source to determine activity.
There have been no changes to the rules in response to this comment. The
commission disagrees that facilities will be determining their own activity
level. Emissions inventories do not generally contain the activity data that
is required by the rule. That is why §101.360 requires that the source
owner certify the activity level to the executive director. The commission
will evaluate the historical activity submitted by facilities to determine
the amount of allowances. The activity data for calculating allocations is
primarily annual fuel usage or product output. These parameters are fundamental
to most companies' cost and profit structure and are usually verifiable by
other data. This information will be audited by commission staff for accuracy
based upon historical records, testing, emissions inventory, and other replicable
emission calculation methodologies as available.
TIP, BCCA, Chevron, Dow, Dynegy, Entergy, Equistar, ExxonMobil, Lyondell,
Phillips 66, REI, TxOGA, TPIEC, Valero, and BASF commented that there is no
reasoned justification for the rate of NO
x
emission
reduction in one-third increments and this rate of reduction is not needed
to meet rate-of-progress requirements. TIP and BASF suggested a 10% reduction
each year from 2003 - 2006 followed by the target allocation in 2007. Texas
Eastern commented that the implementation schedule is too aggressive. TCC
commented that the phase in period should be extended until 2007. TGC recommended
the rule include an option for sources of less than 25 tons per year to propose
an alternative compliance schedule which demonstrates compliance by January
1, 2005. Kinder Morgan recommended that deadline for achieving the initial
one-third reduction for interstate pipeline companies be moved from December
31, 2002 to December 31, 2003. This would allow time to obtain necessary approvals
for design and construction of the modified facilities. TIP, Goodyear, TxOGA,
and GPA commented that a three-year implementation schedule is not technologically
practical or economically feasible and recommended a five-year (2002 - 2007)
implementation schedule. GPA also suggested that the rule contain a provision
for an alternative implementation schedule for IC engines with allowances
of 25 tons per year or less. The alternative schedule must demonstrate compliance
with the rule by January 1, 2005. An individual stated that the implementation
schedule for the cap and trade system is too short and yearly emission reductions
do not realistically reflect the operational and planning schedules of companies.
The rules have been revised based on these comments. The commission believes
that phasing in compliance with these rules is critical to the success of
the program for many reasons including availability of equipment needed to
make reductions as well as the need to satisfy the SIP requirement that reductions
are made as soon as practicable. The designated attainment year in the HGA
area is 2007, and the rules have been revised to require a less rapid reduction
of NO
x
from affected facilities and allow phase
in between 2002 and 2007. The new schedule as described in §101.353 will
ensure that NO
x
emission from stationary facilities
will be reduced to a level necessary to reach attainment.
CAAC commented that the establishment of a final cap should take into account
the controls established to date. A 90% reduction may not be feasible for
a source currently using best available control technology.
The rules were not revised in response to this comment. The 90% reduction
is an estimate of the overall reductions to be achieved from the 1997 emission
inventory for stationary facilities throughout the entire HGA nonattainment
area. The actual requirement which applies to each facility depends upon the
type of facility and is stated in terms of an emission rate, generally not
a percentage reduction. The commission recognizes that some facilities may
have made reductions subsequent to that inventory. These facilities would
only be required to additionally reduce emission to a point that complies
with individual emission specifications contained in the applicable Chapter
117 requirement. In this way, cleaner facilities are not penalized.
Enron and Coalition commented that emission levels under the cap and trade
system should not be established by the type of fuel used but rather by the
industry type, for example power generation. This will encourage the use cost-effective
approaches to emission reductions. Emissions should also be regulated based
on output such as lb/MWh to encourage efficiency. Direct credit should be
available for the benefits of combined heat and power generation.
The rules were not revised in response to this comment. The adopted cap
and trade rules allocate allowances based on the heat input of a facility,
not the production output. This is consistent with the methodology used in
developing the SIP. Because the cap and trade program is a SIP compliance
and flexibility tool for stationary facilities, it is necessary to base the
cap and trade program on identical methodology. Credit for the dual generation
of heat and power is built into the cap and trade program if this results
in reduced emissions. Any facility that achieves a dual result with the same
energy input will use less allowances as a result of this efficiency.
The proposal allows sources newly authorized by permit application or permit
by rule to receive allowances based on their permitted or actual activity
levels. TIP, BCCA, Chevron, Dow, REI, TxOGA, Valero, and BASF support this
concept but commented that newly modified sources should be treated identically.
The rules have been revised based on this comment. The commission agrees
with this comment and has revised §101.353(a) to refer to new and modified
facilities. By "modified facilities" the commission is referring to the modification
itself. For example if an existing facility is modified to double its capacity
in 1998, the emissions from the original facility will be allocated in the
same way as facilities existing before 1997. The increase in emission allowable
associated with the modification will be treated as a facility which did not
exist before 1997.
Calpine and RMT requested clarification of the term "...the source's emission
factor listed in Chapter 117" as it appears in §§101.353(a)(1)(A),
101.353(a)(1)(B), 101.353(a)(2)(B)(i), 101.353(a)(2)(B)(ii), and 101.353(a)(3)(B)(ii).
The commission should clarify §101.353(a)(1)(C) to state the deadline
for submitting an administratively complete application is January 2, 2001.
The rules have been revised in response to this comment. The revised rules
cite the specific sections of Chapter 117 which are relevant. The rules have
also been revised to include the deadline of January 2, 2001 for submitting
an administratively complete application.
Avista-Steag commented that newer and cleaner facilities should not pay
a disproportional amount of the cost to reduce emissions at older facilities.
Because new facilities must obtain allowances prior to operation, they must
purchase allowances from operating facilities that may have upgraded their
equipment to generate surplus allowances. The new facility therefore pays
for a portion of the older facility's upgrade. They also stated that the requirement
for new electric generating plants to purchase allowances before operation
will deter the construction of electric generating capacity in the Houston
area because the purchase must be added onto the cost of implementing lowest
achievable emission rate controls. ED commented that three to five percent
of all allowances be set aside for allocation to operators of sources that
carry out qualifying energy efficiency projects in the region.
No change was made based on this comment. Owners that retrofit older facilities
can recover some costs through the sale of allowances. The commission intended
this as an incentive to reduce emissions from these facilities. While owners
of newer facilities must purchase allowances prior to operation, these facilities
can be constructed to operate cleaner than the older retro-fitted facilities
thus reducing their need for allowances. In some cases, the newer facilities
are at an economic advantage in complying with the point source rules due
to their ability to install state-of-the-art technology instead of retrofitting
older technology. The commission believes this will provide a balanced program
that allows owners to make the appropriate business decision for their facility
within the framework of the required reductions. The commission disagrees
that the need to acquire allowances prior to operation of new facilities will
deter the construction of new electric generating capacity. A growing market
demand for electricity that would support new generating capacity will allow
for a profitable expansion. Operators of facilities that complete energy efficiency
projects that directly affect emissions from their facilities will be able
to generate allowances based on their emission reductions.
The EPA commented that the rule should contain enforcement provisions to
make the rule enforceable and without the provisions the rule cannot be approved.
One individual stated that the program does not have a penalty policy.
The rules were revised in response to this comment. In the event that an
account does not contain a sufficient number of allowances on February 1,
the rules already provide for the automatic subtraction of the amount lacking
plus 10% of a facility's exceedence of its allocations from the subsequent
year's allocations. Additionally violations of this rule are subject to the
normal enforcement actions of the commission for violating rules and regulations
which are subject to administrative penalties up to $10,000 per violation
per day. This was clarified by adding rule language to §101.353(c). The
commission penalty policy is not contained within each rule but is a separate
policy implemented by the enforcement branch of the agency. Penalties are
not generally detailed in the rule so that enforcement staff has flexibility
to make case-by-case decisions.
TIP, Chevron, Dynegy, Entergy, Equistar, ExxonMobil, Lyondell, Phillips
66, REI, TxOGA, TPIEC, Valero, and BCCA commented that allowances should be
allocated for a stream of 30 years or more rather than allocated yearly to
allow for more fluid trading and a defined period, greater than one year,
of overcontrol or undercontrol for participating sites. This methodology would
also simplify allocations.
The commission has made no changes to the rule in response to this comment.
The intent of the HGA SIP, of which this rule is a part, is to attain the
ozone standard. Subsequent to attainment, the commission will be responsible
for a maintenance plan for HGA air quality. Allocation of allowances on a
yearly basis provides the commission the ability to plan and anticipate effects
on air quality. It also provides the commission an enforcement mechanism for
facilities whose actual emissions exceed the allowances in their compliance
account through the reduction of subsequent yearly allocations. The commission
has decided not to allocate a stream of allowances into the future for many
reasons including the amount of tracking that would entail for agency staff.
The commission disagrees that this methodology would simplify allocations.
However, nothing would not prohibit facilities from entering private agreements
for the sale of future allocations or rights to allocations.
The EPA stated that in the absence of an established procedure for the
executive director to approve deviations from allocation methodology, such
deviations will require the EPA approval.
There have been no changes to the rule in response to this comment. The
executive director plans to detail the factors which may be considered for
deviation from allocation methodology in a guidance document which will be
shared with the EPA upon its completion. The executive director plans to limit
deviations to extraordinary circumstances. The commission has revised the
rule to include a deadline for applications for deviation.
TIP, BCCA, Chevron, Dow, Dynegy, Entergy, Equistar, ExxonMobil, Lyondell,
REI, TxOGA, TPIEC, Valero, and BASF commented that the commission should clarify
that target allocation based on 1997 - 1999 activity will not change despite
shutdowns, replacements or changes to equipment. Calpine and RMT stated that
the proposal does not address what happens to allowances allocated to sources
that shut down during a control period. They suggest retaining the allowances
in the emission cap to help sustain economic activity and promote replace
of older units with new, cleaner equipment
The rules have been revised based on this comment. The commenters are correct,
the allocations will not change unless the program is revised in the future.
The commission has added §101.353(h) to state and clarify that allowances
will not change despite shutdowns, replacements, or changes to equipment assuming
the allowances are based on historical activity levels. However, facilities
which obtain allocations based upon allowables but never constructs will not
continue to receive allocations.
BCCA, Phillips 66, RAQCG, and Chevron supports an additional incentive
program that would provide funds for use by a wide range of source categories
to assist compliance with SIP required reductions. Such a fund would be competitive
and, if funded by private sources, would provide appropriate credit or benefit
to the parties providing the funding. The plan should incorporate broad executive
director authority to approve credits on a case-by-case basis.
The rules were not revised based on this comment. The establishment of
a private fund for pollution control projects is outside the scope of the
adopted rules and will be left to the discretion of affected industries. If
projects completed under such a fund result in emission reductions then the
subsequent surplus allowances may be banked or traded under the provisions
of this adoption. The rules are intended to provide market-based flexibility
in meeting emission standards, and the commission prefers to let the market
set the cost of allowances.
Calpine and RMT commented that rule language should be added to specify
that banked allowances will be deducted from accounts before subtracting allowances
calculated under §101.353.
The commission revised §101.354 based on this comment, however the
rule was revised to require allowances most recently allocated to be subtracted
from the compliance account prior to other allowances. By first subtracting
allowances issued for a facility's current control period and limiting the
life of banked allowances to one-year the commission prevents an accumulation
of banked allowances in compliance accounts that would soon jeopardize the
overall system cap. The subtraction of newer credits first ensures that facilities
can't rotate or accumulate credits to circumvent the one-year carryover limit.
BASF, BCCA, Chevron, Dow, Dynegy, Entergy, Equistar, ExxonMobil, Lyondell,
LCR, Peco, Phillips 66, REI, TCC, TxOGA, TPIEC, Valero, and TIP commented
that emission reduction credits (ERCs) should be convertible to allowances
and the proposal lacks reasoned justification why this is not allowed. By
definition all recognized emission credits are real, quantifiable, and surplus
to the SIP. Diamond-Koch recommended including a method of converting ERCs
to DERCs for use as allowances.
No change has been made based on this comment. ERCs and MERCs were intentionally
excluded from §101.356(f) because they would allow a permanent increase
to the NO
x
emission cap that was determined necessary
for the HGA area to reach attainment of the ozone standard. DERCs and MDERCs
were included to provide additional flexibility to the cap because their use
would be short term and not permanent. Additionally, the use of DERCS is limited
during the years 2005, 2006, and 2007 to ensure that the compliance monitoring
is not impacted. For these reasons, the rule was also not revised to allow
ERCs to be converted into DERCs.
TIP, Chevron, Dow, Dynegy, Entergy, Equistar, ExxonMobil, Lyondell, Phillips
66, REI, TxOGA TPIEC, Valero, and BCCA commented that the existing discrete
emission reduction credit (DERC) trading rules require a 10% environmental
contribution and a 5% compliance margin. This requirement has been extended
to the use of DERCs in lieu of allowances. They stated that there is not a
reasoned justification for this requirement and that it is not necessary to
meet a region wide cap.
The commission revised §101.356 based on this comment. The commission
agrees that the cap was set at a level necessary for stationary facilities
as part of the overall attainment strategy for the HGA nonattainment area.
The requirement of retiring an additional 10% of DERCs and MDERCs for an environmental
contribution and an additional 5% for a compliance margin is not required
when using DERCs and MDERCs in lieu of allowances under the HGA cap and trade
program.
TIP, Chevron, Dow, Dynegy, Entergy, Equistar, ExxonMobil, Lyondell, Pasedena,
Peco, Phillips 66, REI, TxOGA, TPIEC, Valero, and BCCA commented that the
rule should contain a provision allowing volatile organic compound (VOC) reductions
in the place of NO
x
allowances where the VOC
reductions are demonstrated to reduce ozone an equal amount.
The commission has modified §101.356 based on this comment. The rule
now states that VOC DERCs or MDERCs may be used in lieu of NO
x
allowances provided that a demonstration has been made and approved
by the executive director and the EPA to show that the use of VOC DERCs or
MDERCs is equivalent to the use of NO
x
allowances
in reducing ozone.
ED commented that sources subject to the cap and trade program should not
be able to use DERCs and MDERCs generated outside the area of program applicability.
The rules were not revised in response to this comment. The commission
agrees that only DERCs and MDERCs generated in the HGA nonattainment area
may be used under the cap and trade program until such time as a demonstration
is made a approved to show that credits generated elsewhere improve the air
quality within the nonattainment area. This ensures that any emissions in
excess of the cap are compensated for in the same air shed. The restriction
may already be found in Chapter 101, Subchapter H, Division 4 and applies
to credits used under the cap.
The EPA commented that the commission should justify the use of mobile
emission credits to meet cap allowances for stationary sources.
The commission has made no changes in response to this comment. The commission
believes that any reduction that is quantifiable, surplus, and real regardless
of the source will result in an improvement in air quality. The commission
further believes that if a reduction occurs that is not relied upon as a reduction
in the SIP, and if that reduction is not required by local, state, or federal
rules and regulations, then that reduction is truly surplus to the SIP and
may be available for use by facilities subject to SIP requirements for flexibility.
The commission has taken measures to ensure that use of credits under the
cap will not impact the attainment demonstration. ERCs and MERCs were intentionally
excluded from use in the cap and trade program because they would allow a
permanent increase to the NO
x
emission cap that
was determined necessary for the HGA area to reach attainment of the ozone
standard. DERCs and MDERCs were included to provide additional flexibility
to the cap because their use would be short term and not permanent. Additionally,
the use of DERCS is limited during the years 2005, 2006, and 2007 to ensure
that the compliance monitoring is not impacted. The ability to use DERCs,
especially MDERCs, will also encourage the development of cleaner technologies
for NO
x
emissions which are not covered by the
cap and trade system. The commission will audit the cap and trade program
on a three year cycle and that audit will include a determination on the effect
of using discrete credits in the program.
The EPA commented that the commission should determine at the end of each
year the effectiveness of the regulation in meeting the emission cap. One
individual stated that the program does not have an ongoing evaluation of
its benefits. TxOGA and Valero recommended the cap and trade program contain
provisions for executive director review and modification, including cost
thresholds for allowances, if the program does not provide the intended flexibility.
The commission has added §101.356(g) based on the EPA's comment. The
new subsection modifies the cap and trade rule to require an audit of the
program every three years. The executive director will also complete a thorough
review of account activity, including quantification of actual emissions,
every year. Any necessary rule changes to improve the cap and trade program
will be made in response to the results of the audit. Since the overall cap
will be shrinking, compliance with the cap will mean a reduction in actual
emissions. Additionally, as noted in the SIP, the commission is planning to
perform a mid-course review of the entire SIP in the 2003 - 2004 time-frame.
At that time the commission will have information regarding the effectiveness
of the cap and trade program, especially as it applies to certain utilities.
The commission does not believe that it is appropriate to identify cost thresholds
now which would be used to evaluate the flexibility provided by the program
in the future.
ED recommended that the commission closely follow the guidance in the EPAs
publication of "NO
x
Budget Trading Program for
State Implementation Plans" in order to gain approval of the plan from the
EPA. They also stated that the program should be reviewed after three years
to determine its effectiveness in reaching the NO
x
emission target.
The rules were revised in response to this comment. The commission reviewed
the EPA guidance and has based this adoption on methodology that is approvable
by the EPA. The commission has also responded to the EPA comments regarding
this adoption. The commission has added §101.356(e) to require an internal
program audit every three years to evaluate the effectiveness of the cap and
trade program.
CAAC commented that allowances should only be banked for one-year and that
there should be no credit for curtailment of activity.
The rules were not changed in response to this comment. The proposal requires
that banked allowances expire after one-year. If curtailment of activity results
in reduced emissions and thus, unused allowances, those allowances may be
banked or traded within the requirements of this division. The cap for stationary
facilities was set at a level necessary as part of an overall strategy for
the HGA area to reach attainment. It is the commission's intent to allow unrestricted
use of allowances regardless of why they were not used. This would include
a facility curtailing its operations so as to not use all of its allowances.
One typical concern with curtailment of activity is that it is temporary and
should not be creditable as an ERC. However, since allowances are for one-
year only, that concern is not relevant. Another concern has been that the
activity is simply shifted to other facilities. However, since the emissions
from point sources are capped that concern is addressed as well.
ED commented that the commission should require emission monitoring no
less stringent than that required under the federal acid rain program.
The rules were not revised in response to this comment. The cap and trade
program has no specific monitoring requirements. Facilities participating
in the program use or will be required to use, if applicable, monitoring methods
required by other state rules and regulations to quantify their actual emissions.
The federal acid rain program applies to a more discrete group of facilities
so creating emission monitoring requirements is more meaningful. However,
NO
x
point sources vary widely and monitoring
requirements should be made in the rule that addresses each category of sources.
TIP, Chevron, Dow, Equistar, REI, TxOGA, Valero, and BCCA commented that
the installation of enhanced monitoring equipment should be delayed until
the cap and trade target allocation year of 2005, and there is no reasoned
justification for advancing the monitoring requirement to 2001, well ahead
of the substantive reductions needed for attainment.
The rules have been changed in response to this comment. The commission
proposed a December 31, 2001 compliance date for installation of emissions
monitors and fuel meters in order to improve the consistency of the value
of a NO
x
allowance at the start of the trading
program and to improve the inputs used in the commission's air quality planning
tools. However, the proposed schedule did not take into account the practicalities
identified by the commenters. Both PEMS and CEMS vendors indicated that the
number of monitors required in one-year would strain their abilities to provide
the equipment. The owners identified clear benefits of installing the monitors
in conjunction with the control equipment. If a CEMS is installed before the
flue gas controls are fully constructed, the CEMS will probably need to be
uninstalled during construction and possibly relocated after NO
x
controls. A PEMS will need to be retrained after the installation
of control equipment. Phasing in CEMS/PEMS with the emission control equipment
is a more rational and cost effective approach and the commission has modified §117.520(c)
to reflect this. Therefore, the rules have been revised to require that the
monitors will be phased over a four and one-quarter year period, at the installation
of emission controls or March 31, 2005 if construction of controls has not
commenced. This phase-in will achieve the end result benefits of specified
emissions reduction by March 31, 2005. Because the first reduction period
has been extended to March 31, 2005, the greater uncertainty about NO
TIP, TxOGA, Valero, and REI commented that the rule should allow the documentation
of allowance trading be accomplished electronically in keeping with modern
commercial practice.
No change was made in response to this comment. The commission agrees with
this comment but it currently limited by available resources. The commission
intends to review the feasibility of implementing this type or similar tracking
as resources become available.
Discrete Emission Reduction Credits Comments
FPL requested clarification as to whether a DERC has an indefinite life
or expires after one-year if it is used as a banked allowance under the cap
and trade program. CPS requested clarification on whether a DERC has an indefinite
period of existence or expires after 60 months as does an ERC.
No changes have been made in response to this comment. DERCs are quantified
as a mass of emissions and may be used until they are gone. Unused DERCs do
not expire after one-year as do allowances under the cap and trade program.
Nor do they expire after 60 months as unused ERCs do.
CPS commented that §101.373(f)(8)(B) be modified to allow the use
of DERCs by any facility regulated under Chapter 117.
No changes have been made in response to this comment. Section 101.373(f)(8)
simply defines the calculation methodology for Chapter 117 sources. It does
not determine which sources may utilize banking to meet Chapter 117 requirements.
The availability of the option to use banking is determined in the section
of the commission's rules which applies the control requirement. For facilities
not already allowed to utilize credits under Chapter 117, a change would require
revisions to the applicable section of Chapter 117.
CPS commented that the formula in §101.373(f)(8)(B) for calculating
DERCs seems to be unnecessary and meaningless because there is no definition
for "proposed level of activity" or "proposed emission rate."
The rules were revised based on this comment. The definition of "level
of activity" was added to §101.370. The commission believes that it is
clear that "proposed" refers to the project being proposed for the generation
of credits.
CPS and TXU commented that the commission should remove the restriction
against the use of DERCs during ozone season in areas of ozone seasons of
less than twelve months.
The rules were not changed in response to this comment. It is crucial in
attainment with the ozone standard that facilities not be able to make reduction
outside of the ozone season which may be used during the ozone season. This
is especially true for sources that have their peak usage during months when
ozone exceedances are most likely.
Sierra-Houston opposed the trading of DERCs outside the area in which they
are generated and stated that each airshed should make its own reductions.
The commission has made no changes in response to this comment. DERCs may
be traded from nonattainment counties to attainment counties and among attainment
counties. Since the area of use is in attainment with the federal air quality
standards, such trading should not harm air quality in these areas and could
help reduce problems in nonattainment areas if the reductions are made there.
DERCs and MDERCs may only be generated and used in nonattainment areas and
no trading may occur between nonattainment areas unless it is shown that emission
reductions in the county of generation will improve air quality in the nonattainment
area of use.
Sierra-Houston opposed the creation of MERCs.
The commission has made no change to the rules in response to this comment.
The generation and use of MERCs and MDERCs provides additional flexibility
for both mobile and stationary sources without impeding progress toward air
quality goals. Additionally, allowing for MERC and MDERC will help to encourage
new mobile source emission reductions technologies which are badly needed.
The emergence of these technologies may allow for requirement of them in the
future if they are needed to meet the NAAQS.
Sierra-Houston oppose DERCs being used to exceed permit allowables.
The commission has made no change to the rules in response to this comment.
The ability to use DERCs to exceed permit allowables is very limited. It is
meant for temporary, short-term increases only. There are restrictions on
use of discrete credits in §101.373(f)(7) to protect against the potential
health impact of the increased uses. Facilities increasing their emissions
by use of DERCs may be subject to a health effects review for any increase
in emissions. Any review would be conducted independently of the trade and
can result in a restriction on the use of credits regardless of the amount
of credits transferred during the trade.
Subchapter A. GENERAL RULES
30 TAC §101.29
STATUTORY AUTHORITY
The repeal is adopted under Texas Health and Safety Code, TCAA, §382.011,
which authorizes the commission to control the quality of the state's air; §382.012,
which authorizes the commission to develop a plan for control of the state's
air; §382.017, which provides the commission the authority to adopt rules
consistent with the policy and purposes of the TCAA, and 42 USC, §7410(a)(2)(A),
which requires SIPs to include enforceable emission limitations and other
control measures or techniques, including economic incentives such as fees,
marketable permits, and auction of emission rights.
This agency hereby certifies that the adoption has been reviewed
by legal counsel and found to be a valid exercise of the agency's legal authority.
Filed with the Office of
the Secretary of State on December 29, 2000.
TRD-200009071
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Effective date: January 18, 2001
Proposal publication date: August 25, 2000
For further information, please call: (512) 239-6087
1.
EMISSION CREDIT BANKING AND TRADING
30 TAC §§101.300-101.304
STATUTORY AUTHORITY
The new sections are adopted under Texas Health and Safety Code, TCAA, §382.011,
which authorizes the commission to control the quality of the state's air; §382.012,
which authorizes the commission to develop a plan for control of the state's
air; §382.017, which provides the commission the authority to adopt rules
consistent with the policy and purposes of the TCAA, and United States Code, §7410(a)(2)(A),
which requires SIPs to include enforceable emission limitations and other
control measures or techniques, including economic incentives such as fees,
marketable permits, and auction of emission rights.
§101.300.Definitions.
The following words and terms, when used in this division, shall have
the following meanings, unless the context clearly indicates otherwise.
(1)
Activity--The amount of activity at a source measured in
terms of production, use, raw materials input, vehicle miles traveled (VMT),
or other similar units that have a direct correlation with the economic output
and emission rate of the source (i.e., mass emitted per unit of activity).
(2)
Actual emissions--Actual emissions as of a particular date
shall equal the total emissions during the selected time period, using the
unit's actual daily operating hours, production rates, types of materials
processed, stored, or combusted during the selected time period.
(3)
Applicable emission point--The source which is either generating
an emission reduction or using an emission credit.
(4)
Area source--Any source included in the agency emissions
inventory under the area source category.
(5)
Baseline--Emissions that occur prior to an emission reduction
strategy, considering all limitations required by applicable state and federal
regulations. The baseline may not exceed the quantity of emissions reported
in the most recent year of emissions inventory used for state implementation
plan (SIP) determinations.
(6)
Baseline activity--The source's level of activity based
on the unit's actual daily operating hours, production rates, or types of
materials processed, stored, or combusted averaged over any consecutive two
calendar year period following or including the most recent year of emissions
inventory used for SIP determinations or subsequent year(s) which precede
the emission reduction strategy or credit use period. For sources in existence
less than 24 months or not having two complete calendar years of activity
data, a shorter time period of not less than 12 months may be considered by
the executive director.
(7)
Baseline emission rate (BER)--The source's rate of emissions
per unit of activity during the baseline activity period.
(8)
Baseline emissions--The source's total actual emissions
based on the product of baseline activity and BER.
(9)
Certified--Any emission reduction that is determined to
be creditable upon review and approval by the executive director.
(10)
Curtailment--A reduction in activity level at any stationary
or mobile source.
(11)
Emission Credit--An emission reduction credit (ERC) or
mobile emission reduction credit (MERC).
(12)
Emission Reduction--An actual reduction of emissions from
a stationary or mobile source.
(13)
Emission reduction credit (ERC)--A certified emission
reduction that is created by eliminating future emissions, quantified during
or before the period in which emission reductions are made, and expressed
in tons per year.
(14)
Emission reduction strategy--The method implemented to
reduce the source's emissions which are surplus.
(15)
Generator--The owner or operator of a source that creates
an emission reduction.
(16)
Mobile emissions baseline--Mobile emissions that occur
prior to a mobile emission reduction strategy, considering all limitations
required by applicable state and federal regulations. A valid mobile emission
baseline can be calculated by either using measured emissions of an appropriately
sized sample of the participating mobile sources using an approved United
States Environmental Protection Agency (EPA) test procedure or by using estimated
emissions of the participating mobile sources using the most recent edition
of EPA's on-road or non-road mobile emissions factor models, or other model
as applicable. To ensure that mobile credits are surplus, mobile source baseline
emissions estimates for each year of the proposed mobile source control program
must be the same as, or lower than, those used, or proposed to be used, in
the SIP in which the control program is proposed.
(17)
Mobile emission reduction credit (MERC or mobile credit)--A
credit representing the amount of emission reductions from a mobile source
strategy. These emission reductions are voluntary and must be in addition
to compliance with requirements of state and federal regulations. MERCs are
any enforceable, permanent, and quantifiable emission reduction (exhaust and/or
evaporative) generated by a mobile source, which has been banked in accordance
with the rules of the commission. MERCs can be banked, purchased, traded,
and sold to meet clean air mandates for specified air programs, and MERCs
may be applied to the emission reduction obligations of another air quality
source or to air quality attainment goals. MERCs are expressed in tons per
year.
(18)
Mobile source--On-road (highway) vehicles (e.g., automobiles,
trucks and motorcycles) and non- road vehicles (e.g., trains, airplanes, agricultural
equipment, industrial equipment, construction vehicles, off-road motorcycles,
and marine vessels).
(19)
Mobile source baseline activity--Will be based on an estimate
for each year for which the credits are to be generated. After the initial
year, the annual estimates should reflect:
(A)
the change in the mobile source emissions to reflect any
deterioration in the emission control performance of the participating source;
(B)
the change in the number of mobile sources resulting from
normal retirement or attrition, and the replacement of retired mobile sources
with newer and/or cleaner mobile sources;
(C)
the change in usage levels, hours of operation or VMT in
the participating population; and
(D)
the change in the expected useful life of the participating
population.
(20)
Mobile source baseline emission--The source's total actual
mobile source emissions based on the product of mobile source action and the
mobile source emissions rate.
(21)
Most stringent allowable emissions rate--The emission
rate of a source, considering all limitations required by applicable local,
state, and federal regulations.
(22)
Ozone season--The portion of the year when ozone monitoring
is federally required to occur in a specific geographic area.
(23)
Permanent--An emission reduction that is long-lasting
and unchanging for the remaining life of the source. Such a time period must
be enforceable.
(24)
Protocol--A replicable and workable method of estimating
emission rates or activity levels used to calculate the amount of emission
reduction generated or credits required for stationary or mobile sources.
(25)
Quantifiable--An emission reduction that can be measured
or estimated with confidence using replicable methodology.
(26)
Real reduction--A reduction in which actual emissions
are reduced as opposed to a reduction in allowable emissions.
(27)
Shutdown--The permanent cessation of an activity producing
emissions at a facility.
(28)
Source--As defined in §101.1(90) of this title (relating
to Definitions).
(29)
Surplus--An emission reduction that is not otherwise required
of a source by any local, state or federal law, regulation, or agreed order.
(30)
User--The owner or operator of a source that acquires
and uses emission credits to meet a regulatory requirement, demonstrate compliance,
or offset an emission increase.
§101.302.General Provisions.
(a)
Applicable pollutants. Reductions of volatile organic compounds
(VOCs) and nitrogen oxides (NO
x
) may qualify
as emission credits. Reductions of other pollutants do not qualify as emission
credits under this division. Reductions of one pollutant may not be used to
meet the requirements of another pollutant, except at such time as urban airshed
modeling demonstrates that one ozone precursor may be substituted for another,
subject to executive director and the United States Environmental Protection
Agency approval.
(b)
Emission reduction requirements.
(1)
emission reduction credits (ERCs) are generated from reductions
beyond those required. To be certified as an emission credit, an emission
reduction must be enforceable, permanent, quantifiable, real, and surplus.
The emission credit must be surplus at the time it is created, as well as
when it is used. The certified reduction must have occurred after the most
recent year of emissions inventory used for state implementation plan (SIP)
determinations for VOC and NO
x
, and the source's
annual emissions prior to the emission credit application must have been reported
or represented in the emissions inventory used for SIP determinations.
(2)
mobile emission reduction credits (MERCs) are generated
from reductions beyond those required, and derived from a calculation of the
annual difference between the mobile source emissions baseline and the projected
emissions level after the MERC strategy has been put in place. To be certified
as a MERC, an emission reduction must be enforceable, permanent, quantifiable,
real, and surplus. The emission credit must be surplus at the time it is created,
as well as when it is used. The certified reduction must have occurred after
the most recent year of emissions inventory used for SIP determinations for
VOC and NO
x
, the mobile source's emissions must
have been represented in the emissions inventory used for SIP determinations,
and the applicable mobile sources must have been included in the attainment
demonstration baseline.
(3)
Emission reductions from a source which are certified as
emission credits under this division cannot be recertified in whole or in
part as credits under another division within this subchapter.
(c)
Eligible sources. The following sources are eligible to
generate emission credits:
(1)
stationary sources (including area sources);
(2)
any mobile source;
(3)
any stationary source (including area sources) or mobile
source associated with actions by federal agencies under §101.30 of this
title (relating to Conformity of General Federal Actions to State Implementation
Plans).
(d)
Life of an emission credit.
(1)
If an ERC is used prior to its expiration date, the ERC
is effective for the life of the applicable user source.
(2)
Effective January 2, 2001, an ERC is available for use
for 60 months from the date of the emission reduction except to the extent
regulatory changes occur after the date of reduction that reduce the certified
amount or invalidate the entire reduction for affected emission points. ERCs
certified or applied for prior to January 2, 2001 shall be available for use
for 120 months from the date of the emission reduction except to the extent
regulatory changes occur after the date of the emission reduction that reduce
the certified amount or invalidate the entire reduction for affected emission
points.
(e)
Geographic scope. Only emission reductions generated in
ozone nonattainment areas can be certified. The trading of emission credits
may be discontinued by the executive director in whole or in part and in any
manner, with commission approval, as a remedy for problems resulting from
trading in a localized area of concern. An emission credit must be used in
the nonattainment area in which it is generated unless:
(1)
a demonstration has been made and approved by the executive
director and the United States Environmental Protection Agency (EPA) to show
that the emission reductions achieved in another county, state, or nation
provide an improvement to the air quality in the county of use; or
(2)
the emission credit was generated in an ozone nonattainment
area which has an equal or higher nonattainment classification than the ozone
nonattainment area of use, and a demonstration has been made and approved
by the executive director and the EPA to show that the emissions from the
ozone nonattainment area where the emission credit is generated contribute
to a violation of the national ambient air quality standard in the ozone nonattainment
area of use; or
(3)
the user has obtained prior written approval of the executive
director and the EPA.
(f)
The registry. All emission credit generators and users
must register with the executive director. A notice submitted by a generator
or user will be posted to the registry. The registry will assign a unique
number to each certificate which will include the amount of emission reductions
generated. The registry will maintain current listings of all credits available
or used for each ozone nonattainment area.
(g)
Recordkeeping. The user must maintain a copy of all notices
and backup information submitted to the registry during, and for at least
two years after, the beginning of the use period. The user must also make
such records available upon request to representatives of the executive director,
United States Environmental Protection Agency (EPA), and any local enforcement
agency. The records shall include, but not necessarily be limited to:
(1)
the name, emission point number, and facility identification
number of each unit using emission credits;
(2)
the amount of emission credits being used by each unit;
and
(3)
the specific number, name, or other identification of emission
credits used for each unit.
(h)
Public information. All information submitted with a notice
or report regarding the nature and quantity of emissions associated with the
use or generation of an emission credit is public information and may not
be submitted as confidential. Any claim of confidentiality for this type of
information, or failure to submit all information, may result in the rejection
of the emission reduction. All non-confidential notices and information regarding
the generation, use, and availability of emission credits may be obtained
from the executive director.
(i)
Authorization to emit. An emission credit created under
this division is a limited authorization to emit VOC and/or NO
x
, unless otherwise defined, in accordance with the provisions of this
section, the Federal Clean Air Act, and the Texas Clean Air Act, as well as
regulations promulgated thereunder. An emission credit does not constitute
a property right. Nothing in this division may be construed to limit the authority
of the commission or the EPA to terminate or limit such authorization.
(j)
Program participation. The executive director has the authority
to prohibit an organization from participating in emission credit trading
either as a generator or user, if the executive director determines that the
organization has violated the requirements of the program or abused the privileges
provided by the program.
§101.303.Protocols.
(a)
All source categories must use a EPA approved protocol
if one exists for the applicable source. If the source wants to deviate from
an EPA approved protocol, EPA approval is required before the protocol can
be used.
(b)
If an EPA approved protocol does not exist, the following
applies.
(1)
Emission reduction credits (ERC)--The amount of emission
credits in tons per year will be determined and certified based on actual
monitoring results, when available, or otherwise calculated using good engineering
practices including calculation methodologies in general use in new source
review (NSR) permitting. The source must collect relevant data sufficient
to characterize the process emissions of the affected pollutant and the process
activity level for all representative phases of source operation during the
period under which emission credits are created or used.
(2)
Mobile emission reduction credits (MERC)--The amount of
emission credits in tons per year will be determined and certified based on
actual monitoring results, when available, or otherwise calculated using good
engineering practices. The generator must collect relevant data sufficient
to characterize the process emissions of the affected pollutant, and the process
activity level for all representative phases of mobile source operation during
the period under which mobile credits are created.
(c)
Emission credit generation.
(1)
ERCs may be generated using one of the following methods
or any other method that is approved by the executive director:
(A)
the permanent shutdown of a facility which causes a loss
of capability to produce emissions;
(B)
the installation and operation of pollution control equipment
which reduces emissions below the level required of the emission source;
(C)
a change in a manufacturing process which reduces emissions
below the level required of the emission source;
(D)
the permanent curtailment in production, which reduces
the source's capability to produce emissions;
(E)
pollution prevention projects that produce surplus emission
reductions.
(2)
MERCs may be generated by any mobile source emission reduction
strategy that creates actual mobile source emission reductions under this
rule, and subject to the approval of the commission.
(d)
Emission credit calculation.
(1)
The quantity of ERCs is determined by subtracting the source's
new allowable emission limit (tons per year) from the emission source's baseline
emissions. The source's new allowable emission limit equals the enforceable
emission limit for the applicable emission point after the emission reduction
strategy has been implemented.
(2)
The quantity of MERCs must be calculated from the annual
difference between the mobile source emissions baseline and the projected
emissions level after the MERC strategy has been put in place. The projected
emissions must be based on the best estimate of the actual in-use emissions
of the replacement or substitute on-road or non-road vehicles or transportation
system. Any estimate of a projected annual mobile source emissions level based
on an assumption of reduced consumer service or transportation service would
not be allowed without the support of a convincing analytical justification
of the assumption. Emission baselines for quantifying MERCs should include
the following information and data as appropriate, but not be limited to:
(A)
the emission standard to which the mobile source is subject
or emission performance to which the mobile source is certified;
(B)
the estimated or measured in-use emissions levels per unit
of use from all significant mobile source emissions sources;
(C)
the number of mobile sources in the participating group;
(D)
the type or types of mobile sources by model year;
(E)
the actual or projected activity level, hours of operation
or miles traveled by type, and model year; and
(F)
the projected remaining useful life of the participating
group of mobile sources.
(3)
Emission credits cannot be generated from a source if the
emissions have been transferred from that source to another source.
(e)
Emission credit registration and certification.
(1)
Stationary sources with potential ERCs must submit an ERC
application (EC-1 Form), within 180 days of the implementation of the emission
reduction strategy to the executive director. Sources that have implemented
a strategy prior to the effective date of this rule, must submit an application
by June 1, 2001. Applications will be subjected to a review to determine the
credibility of the reductions. Reductions determined to be creditable will
be certified by the executive director and an ERC certificate will be issued
to the owner.
(2)
Mobile sources with potential MERCs must submit an emission
credit application (EC-1 Form), within 180 days of implementation of the strategy
to the Executive director if an obligation is exceeded, or if it is clearly
demonstrated that actual mobile emission reductions are generated. Sources
that have implemented a strategy prior to the effective date of this rule,
must submit an application by June 1, 2001. The commission will then issue
a MERC certificate(s) to the person, company, business, organization, or public
entity generating the mobile emission reduction, upon approval of the application.
A MERC certificate will be issued by the executive director which indicates
the total amount of certified emission credits, the quantity available on
an annual basis, and the date upon which the last annualized emission reduction
expires.
(3)
The application for a stationary source generator must
include the following information, where applicable for either an ERC or MERC,
on the EC-1 Form for each pollutant reduced at each applicable emission point:
(A)
the name, address, county, telephone number, contact person,
permit or permit by rule numbers, account number of the generator, and the
unique facility identification number and emission point number of the applicable
emission points;
(B)
the name of the owner and/or operator of the generator
source;
(C)
the date of the reduction;
(D)
a complete description of the generation activity;
(E)
for shutdown or permanent curtailment emission reduction
strategies, an explanation as to whether production shifted from the shut
down facility to another facility in the same nonattainment area;
(F)
the amount of emission credits generated;
(G)
for volatile organic compound (VOC) reductions, a list
of the specific compounds reduced;
(H)
the baseline emission activity, baseline emission rate,
baseline total emissions, emissions inventory data from the most recent year
of emissions inventory used for state implementation plan determinations and
emissions inventory data for the two consecutive years used to determine baseline
activity for each applicable pollutant and emission point;
(I)
the most stringent emission rate and the most stringent
emission level for the applicable emission point, considering all the local,
state, and federal applicable regulatory and statutory requirements,
(J)
a complete description of the protocol used to calculate
the emission reduction generated;
(K)
the actual calculations performed by the generator to determine
the amount of emission credits generated; and
(L)
a statement that the emission reductions on which the emission
credits are based are real, surplus, and are based on an eligible emission
reduction strategy listed in subsection (c)(1) of this section.
(4)
The application for a mobile source strategy must include
the following information, where applicable for either an ERC or MERC, on
the EC-1 Form for each pollutant reduced at each applicable mobile source
strategy:
(A)
the name, address, county, telephone number, and contact
person;
(B)
the name of the owner and/or operator of the generator
source;
(C)
the date of the reduction;
(D)
a complete description of the generation activity;
(E)
the amount of emission credits generated;
(F)
the mobile source baseline emission activity, mobile source
baseline emission rate, mobile source baseline total emissions, and the mobile
source strategy;
(G)
a complete description of the protocol used to calculate
the emission reduction generated;
(H)
the actual calculations performed by the generator to determine
the amount of emission credits generated; and
(I)
a statement that the emission reductions on which the emission
credits are based are real, surplus, and based on an eligible emission reduction
strategy that is not prohibited.
(5)
The applicant will be notified in writing if the executive
director denies the emission credit application. The applicant may submit
a revised application at any time.
(f)
Emission credit practices.
(1)
The amount of emission credits in tons per year will be
determined and certified, to the nearest tenth of a ton per year.
(2)
ERCs are based on EPA methodologies, when available, actual
monitoring results, when available, or otherwise calculated using good engineering
practices including calculation methodologies in general use and accepted
in NSR permitting. The executive director shall have the authority to inspect
and request information to assure that the emissions reductions have actually
been achieved.
(3)
MERCs will be determined and certified using:
(A)
EPA methodologies, when available;
(B)
actual monitoring results, when available;
(C)
otherwise calculated using the most current EPA MOBILE
model or other model as applicable; or
(D)
otherwise calculated using creditable emission reduction
measurement or estimation methodologies which satisfactorily address the analytical
uncertainties of mobile source emissions reduction strategies.
(4)
All emission credits are deposited in the registry and
reported as available credits by the Emissions Banking and Trading Program
until they are used, withdrawn, or expire.
(5)
Compliance burden and enforcement.
(A)
ERCs will be made enforceable by one of the following methods:
(i)
amending or altering an NSR permit to reflect the emission
reduction and set a new maximum allowable emission limit;
(ii)
voiding an NSR permit when an emission source has been
shut down;
(iii)
registering on a PI-8 form the emission reduction and
the new maximum allowable emission limit for any facility which is authorized
by a standard exemption or permit by rule;
(iv)
registering on an OPCRE-1 Form the emission reduction
and the new maximum allowable emission limit for any facility which is not
required to have a permit or qualifies for a permit by rule; or
(v)
obtaining an agreed order which sets a new maximum allowable
emission limit for a facility which is not required to have a permit or qualify
for a permit by rule.
(B)
MERCs will be made enforceable by one of the following
methods:
(i)
by registering, on a commission-provided form (MERC-1),
that the MERCs are permanent, quantifiable, real, and surplus; or
(ii)
by obtaining an agreed order which sets a new maximum
allowable mobile source emission limits, which is not required to be implemented
by a rule.
(6)
Unless there are permits under the same commission account
number which contain a condition or conditions precluding such use, ERCs may
be used as the following:
(A)
offsets for a new source or major modification to an existing
source;
(B)
mitigation offsets for action by federal agencies under §101.30
of this title (relating to Conformity of General Federal Actions to State
Implementation Plans);
(C)
an alternative means of compliance with VOC and NO
(D)
netting by the original applicant, if not used, sold, or
otherwise relied upon; or
(E)
other provisions as allowable within the guidelines of
local, state, and federal laws.
(7)
MERCs may only be used for the following purposes:
(A)
an alternative means of compliance with VOC and NO
(B)
complying with fleet requirements to the extent allowed
by the Texas Clean Fleet Program requirements for motor vehicle fleets;
(C)
providing offsets for a new major source or major modifications;
(D)
mitigation offsets for action by federal agencies under §101.30
of this title; or
(E)
other provisions as allowable within the guidelines of
local, state, and federal laws.
(8)
The calculation of the number of ERCs or of MERCs needed
by the user for offsets or for compliance with Chapter 115 or Chapter 117
of this title are as follows:
(A)
for emission credits used as offsets, the method for determining
the number of emission credits needed by the user for offsets is provided
in §116.150 of this title (relating to New Major Source or Major Modification
in Ozone Nonattainment Area); or
(B)
for emission credits used as compliance with Chapter 114,
Chapter 115, or Chapter 117 of this title, the number of emission credits
needed should be determined in accordance with the requirements of this section
plus an additional 10% to be retired as an environmental contribution; or
(C)
for emission credits used to comply with §117.210
of this title (relating to Source Cap) and §117.223 of this title (relating
to Source Cap), sources may reduce the amount of emission reductions otherwise
required by complying with the following equations instead of the equations
in §117.210(c)(1) and (2) and §117.223(b)(1) and (2) of this title.
Figure: 30 TAC §101.303(f)(8)(C)
(D)
emission reductions used as compliance with any other applicable
program should be determined in accordance with the requirements of the appropriate
chapter and section and must contain at least 10% extra to be retired as an
environmental contribution.
(9)
Review schedule.
(A)
For emission credits which are to be used for compliance
with the requirements of Chapter 114, Chapter 115, or Chapter 117 of this
title, the user must submit a Notice of Intent to Use, (EC-3 Form) at least
90 days prior to the planned utilization of the emission credit. Emission
credits may be utilized only after the executive director grant approval of
the notice of intent to use.
(B)
For emission credits which are to be used as offsets in
accordance with Chapter 116 of this title, the user must submit a Notice of
Intent To Use Form (EC-3 Form), along with the emission credit certificate
when providing the emission credits as offsets.
(10)
Emission credits are freely transferable in whole or in
part, and may be traded or sold to a new owner any time before the expiration
date of the emission credit. The Emissions Banking and Trading Program must
be notified by means of an EC-4 Form prior to the transfer. The old certificate
must be submitted to the registry. The executive director will issue a new
certificate to the emission credit purchaser reflecting the emission credits
purchased by the new owner, and a revised certificate to the emission credit
seller showing any remaining emission credits available to the original owner.
Emission credits may be transferrable only after the executive director grants
approval of the transaction.
(11)
Emission credits may be withdrawn from the registry by
the owner at any time prior to the expiration date of the credit and may be
held by the owner. Emission credits may still be used by the original owner
as an emission reduction for netting purposes after the emission credits have
expired, as provided in §116.150 of this title.
(12)
Recording use of emission credits.
(A)
Emission credits to be used as offsets in an NSR permit
must be identified prior to permit issuance. The original certificate must
be submitted prior to operation.
(B)
Use of emission credits for purposes other than those specified
in subparagraph (A) of this paragraph may not commence until the user has
received approval from the executive director. The user must also keep a copy
of the emission credit certificate, the notice, and all backup in accordance
with §101.303(e) of this section.
(C)
If the executive director denies the stationary source's
use of emission credits, any person affected by the executive director's decision
may file a motion for reconsideration within 60 days of the denial. Notwithstanding
the applicability provisions of §50.31(c)(7) of this title (relating
to Purpose and Applicability), the requirements of §50.39 of this title
(relating to Motion for Reconsideration) may apply. Only a person affected
may file a motion for reconsideration.
This agency hereby certifies that the adoption
has been reviewed by legal counsel and found to be a valid exercise of the
agency's legal authority.
Filed
with the Office of the Secretary of State on December 29, 2000.
TRD-200009072
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Effective date: January 18, 2001
Proposal publication date: August 25, 2000
For further information, please call: (512) 239-6087
30 TAC §§101.350-101.354, 101.356, 101.358-101.360
STATUTORY AUTHORITY
The new sections are adopted under Texas Health and Safety Code, TCAA, §382.011,
which authorizes the commission to control the quality of the state's air; §382.012,
which authorizes the commission to develop a plan for control of the state's
air; §382.017, which provides the commission the authority to adopt rules
consistent with the policy and purposes of the TCAA, and United States Code, §7410(a)(2)(A),
which requires SIPs to include enforceable emission limitations and other
control measures or techniques, including economic incentives such as fees,
marketable permits, and auction of emission rights.
§101.350.Definitions.
The following words and terms, when used in this division, shall have
the following meanings, unless the context clearly indicates otherwise.
(1)
Allowance--The authorization to emit one ton of nitrogen
oxides (NO
x
), expressed in tenths of a ton, during
a control period.
(2)
Authorized account representative--The responsible person
who is authorized, in writing, to transfer and otherwise manage allowances.
(3)
Banked allowance--An allowance which is not used to reconcile
emissions in the designated year of allocation, but which is carried forward
for up to one year and noted in the compliance or broker account as "banked."
(4)
Broker--A person not required to participate in the requirements
of this division who opens an account under this division for the purpose
of banking and trading allowances.
(5)
Broker account--The account where allowances held by a
broker are recorded. Allowances held in a broker account may not be used to
satisfy compliance requirements for this division.
(6)
Compliance account--The account where allowances held by
a facility or multiple facilities at a single site are recorded for the purposes
of meeting the requirements of this division.
(7)
Control period--The 12-month period beginning January 1
and ending December 31 of each year. The initial control period begins January
1, 2002.
(8)
Houston/Galveston (HGA) ozone nonattainment area--As defined
in §101.1 of this title (relating to Definitions).
(9)
Level of activity--The amount of activity at a source measured
in terms of production, fuel use, raw materials input, or other similar units
that have a direct correlation with the economic output and emission rate
of the source (i.e., mass emitted per unit of activity).
(10)
Person--For the purpose of issuance of allowances under
this division, a person includes an individual, a partnership of two or more
persons having a joint or common interest, a mutual or cooperative association,
or a corporation.
(11)
Site--As defined in §122.10 of this title (relating
to General Definitions).
§101.351.Applicability.
This division applies to all stationary facilities which emit nitrogen
oxides (NO
x
) in the Houston/Galveston nonattainment
area and are subject to the emission specifications under §§117.106,
117.206, and 117.475 of this title (relating to Emission Specifications for
Attainment Demonstration; Emission Specifications for Attainment Demonstration;
and Emission Specifications) and which have a design capacity to emit ten
tons or more per year of NO
x
.
§101.352.General Provisions.
(a)
Allowances are valid only for the purposes described in
this division and cannot be used to meet or exceed the limitations of any
annual emission limitation authorized under Chapter 116, Subchapter B, of
this title (relating to New Source Review Permits), or any other applicable
rule or law.
(b)
Beginning February 1, 2003, and no later than February
1 following the end of every control period, each site, shall hold a quantity
of allowances in its compliance account that is equal to or greater than the
total emissions of nitrogen oxides emitted during the control period just
ending. Compliance with this division will begin with the initial control
period beginning January 1, 2002.
(c)
Unused allowances can be certified as emission reduction
credits (ERCs), provided that:
(1)
an enforceable and permanent reduction of annual allowances
is approved by the executive director; and
(2)
all applicable requirements of Division 1 of this subchapter
(relating to Emission Credit Banking and Trading) are met.
(d)
Allowances cannot be used for netting requirements under
Chapter 116, Subchapter B, Divisions 5 and 6 of this title (relating to Nonattainment
Review and Prevention of Significant Deterioration Review).
(e)
Allowances may be used simultaneously to satisfy the correlating
one to one portion of offset requirements for new or modified facilities subject
to federal nonattainment NSR requirements as provided in Chapter 116, Subchapter
B, Division 7 of this title (relating to Emission Reductions Offsets).
(f)
An allowance does not constitute a security or a property
right.
(g)
All allowances will be allocated, transferred, or used
in tenths of tons. To determine the number of allowances, the number of allowances
will be rounded down to the nearest tenth when determining excess allowances
and rounded up to the nearest tenth when determining allowances used.
(h)
One compliance account shall be used for multiple facilities
required to participate under this division and located at the same site and
under common ownership or control.
(i)
The commission will maintain a registry of the allowances
in each compliance account. The registry will not contain proprietary information.
§101.353.Allocation of Allowances.
(a)
Allowances will be deposited into compliance accounts according
to the following equation except as provided in subsection (g) of this section.
Figure: 30 TAC §101.353(a)
(b)
For a new and/or modified facility that has submitted,
under Chapter 116 of this title, an application which the executive director
has not determined to be administratively complete before January 2, 2001,
or has qualified for a permit by rule under Chapter 106 of this title and
has not commenced construction before January 2, 2001, allowances for each
control period or the annual allocation rights shall be acquired from facilities
already participating under this division, or in accordance with §101.356(d)
of this title (relating to Allowance Banking and Trading).
(c)
If actual emissions of NO
x
during a control period exceed the amount of allowances held in a compliance
account on February 1 following the control period, allowances for the next
control period will be reduced by an amount equal to the emissions exceeding
the allowances in the compliance account plus an additional 10%. This does
not preclude additional enforcement action by the executive director.
(d)
Allowances will be allocated by the executive director,
who will deposit allowances into each compliance account:
(1)
initially, by January 1, 2002;
(2)
subsequently, by January 1 of each following year.
(e)
The annual deposit for any control period may be adjusted
by the executive director to reflect new or existing state implementation
plan requirements.
(f)
Allowances may be added or deducted by the executive director
from compliance accounts following the review of reports required under §101.359
of this title (relating to Reporting).
(g)
In extenuating circumstances, the executive director may
deviate from the requirements of this section to determine the amount of allowances
to be allocated to a facility. Applications to seek deviation must be submitted
by the owner or operator of the facility in discussion to the executive director
no later than June 30, 2001.
(h)
Allowances calculated under subsection (a) of this section
will continue to be based on historical activity levels, despite subsequent
reductions in activity levels. If allowances are being allocated based on
allowables and the facility does not achieve two complete consecutive calender
years of actual level of activity data, then allowances will not continue
to be allocated if the facility ceases operation or is not built.
§101.354.Allowance Deductions.
(a)
Allowances will be deducted in tenths of a ton from a site's
compliance account for a control period based upon the following equation
or other method as determined by the executive director.
Figure: 30 TAC §101.354(a)
(b)
When deducting allowances from a site's compliance account
for a control period, the executive director will deduct the allowances beginning
with the most recently allocated allowances before deducting banked allowances.
(c)
Allowances allocated in accordance with the variables in
(a)(2)(B) listed in Figure 30 TAC §101.353(a) may only be used by the
facility for which they were allocated and may not be used by other facilities
at the same site during the same control period.
(d)
On February 1 after every control period, a site shall
hold a quantity of allowances in its compliance account that is equal to or
greater than the total NO
x
emissions emitted
during the prior control period.
§101.356.Allowance Banking and Trading.
(a)
Allowances not used for compliance at the end of a control
period may be banked for use in the following control period in compliance
with §101.354 of this title (relating to Allowance Deductions) or traded
except as provided in subsection (c) of this section.
(b)
Allowances which have not expired or been used may be traded
at any time during a control period after they have been allocated except
as provided in subsection (c) of this section.
(c)
Allowances not used for compliance during a control period
which were allocated in accordance with the variables in (a)(2)(B) and (3)(B)
listed in Figure 30 TAC §101.353(a) may not be banked for future use
or traded.
(d)
Only authorized account representatives may trade allowances.
(e)
Trades shall be completed by the executive director following
the submittal of a completed ECT-2 Form, Application for Transfer of Allowances.
The completed ECT-2 shall include the price paid per allowance and shall be
submitted to executive director at least 30 days prior to the allowances being
deposited into the transferee's broker or compliance account. The executive
director will issue a letter to the purchaser and seller reflecting this trade.
The trade will be considered finalized upon issuance of this letter.
(f)
Sites may use nitrogen oxides (NO
x
) discrete emission reduction credits (DERCs) or mobile discrete emission
reduction credits (MDERCs) which have been generated and, acquired, in accordance
with Division 4 of this subchapter (relating to Discrete Emission Credit Banking
and Trading) in place of allowances for compliance with this division in accordance
with paragraphs (1)-(7) of this subsection. Sites may use volatile organic
compound (VOC) DERCs or MDERCs which have been generated and acquired in accordance
with Division 4 of this subchapter, in place of allowances for compliance
with this division in accordance with paragraphs (1)-(7) of this subsection
provided that demonstration has been made and approved by the executive director
and the United States Environmental Protection Agency to show that the use
of VOC DERCs or MDERCs is equivalent, on a one to one basis or other ratio,
to the use of NO
x
allowances in reducing ozone.
(1)
MDERCs may be used in lieu of allowances at a ratio of
one MDERC for one allowance.
(2)
Prior to January 1, 2005, DERCs generated prior to January
1, 2005 may be used at a ratio of one DERC for one allowance.
(3)
Beginning January 1, 2005, DERCs generated prior to January
1, 2005 may be used in lieu of allowances at a ratio of ten DERCs for one
allowance.
(4)
DERCs generated on or after January 1, 2005 may be used
in lieu of allowances at a ratio of one DERC for one allowance.
(5)
Beginning January 1, 2005, no more than 10,000 DERCs may
be used in any combination totaled over all sites in the HGA ozone nonattainment
area during a single calender year. This restriction does not apply to MDERCs.
(6)
The 10% environmental contribution and the 5% compliance
margin of Division 4 of this subchapter shall not apply.
(7)
DERCs or MDERCs submitted with a notice of intent to use,
DEC-2 Form, for the purpose of compliance with this section, must be submitted
to executive director at least 30 days prior to intended use.
(g)
Program Audits. No later than three years after the effective
date of this division, and every three years thereafter, the executive director
will audit this program.
(1)
The audit will evaluate the impact of the program on the
state's attainment demonstration, the availability and cost of allowances,
compliance by the participants, and any other elements the executive director
may choose to include.
(2)
The executive director will recommend measures to remedy
any problems identified in the audit. The trading of allowances, discrete
emission reduction credits, and/or mobile discrete emission reduction credits
may be discontinued by the executive director in part or in whole and in any
manner, with commission approval, as a remedy for problems identified in the
program audit.
(3)
The audit data and results will be completed and submitted
to the United States Environmental Protection Agency and made available for
public inspection within six months after the audit begins.
§101.358.Emission Monitoring and Compliance Demonstration.
(a)
Monitoring data or other emission quantifications for facilities
required to monitor or quantify emissions under any other federal or state
program shall be used to show compliance with this division.
(b)
Facilities not required to monitor or quantify nitrogen
oxides emissions shall calculate emissions using good engineering practices,
including calculation methodologies in general use and accepted in new source
review permitting.
§101.359.Reporting.
Beginning March 31, 2003, for each control period, facilities under
each compliance account shall submit a completed ECT-1 Form, Annual Compliance
Report, to the executive director by March 31 of each year detailing the following:
(1)
the amount of actual nitrogen oxides (NO
x
) emissions during the preceding control period;
(2)
the method of determining NO
x
emissions, including, but not limited to, any monitoring protocol and results,
calculation methodology, level of activity, and emission factor; and
(3)
a summary of all final trades for the preceding control
period.
§101.360.Level of Activity Certification.
(a)
The owner or operator of any facility subject to this division
shall certify, no later than June 30, 2001, its historical level of activity
by submitting to the executive director a completed ECT-3 Form, Level of Activity
Certification, along with any supporting information such as usage records,
testing or monitoring data, and production records as follows:
(1)
for facilities in operation prior to January 1, 1997, the
level of activity averaged over 1997, 1998, and 1999;
(2)
for new and modified facilities not in operation prior
to January 1, 1997 and either have submitted, under Chapter 116 of this title
(relating to Control of Air Pollution by Permits for New Construction or Modification),
an application which the executive director has determined to be administratively
complete before January 2, 2001, or have qualified for a permit by rule under
Chapter 106 of this title (relating to Permits by Rule) and have commenced
construction before January 2, 2001, the level of activity authorized by the
executive director.
(b)
The owner or operator of any facility subject to this division
who has certified a facility's level of activity under subsection (a)(2) of
this section shall certify, no later than 90 days from the end of its second
complete calendar year of operation, its first two complete consecutive calender
years of actual level of activity by submitting to the executive director
a completed ECT-3 Form, Level of Activity Certification, along with any supporting
information such as usage records, testing or monitoring data, and production
records.
This agency hereby certifies that the adoption has been reviewed
by legal counsel and found to be a valid exercise of the agency's legal authority.
Filed
with the Office of the Secretary of State on December 29, 2000
TRD-200009073
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Effective date: January 18, 2001
Proposal publication date: August 25, 2000
For further information, please call: (512) 239-6087
30 TAC §§101.370-101.374
STATUTORY AUTHORITY
The new sections are adopted under Texas Health and Safety Code, TCAA, §382.011,
which authorizes the commission to control the quality of the state's air; §382.012,
which authorizes the commission to develop a plan for control of the state's
air; §382.017, which provides the commission the authority to adopt rules
consistent with the policy and purposes of the TCAA, and United States Code, §7410(a)(2)(A),
which requires SIPs to include enforceable emission limitations and other
control measures or techniques, including economic incentives such as fees,
marketable permits, and auction of emission rights.
§101.370.Definitions.
The following words and terms, when used in this division, shall have
the following meanings, unless the context clearly indicates otherwise.
(1)
Activity--The amount of activity at a source measured in
terms of production, use, raw materials input, vehicle miles traveled, or
other similar units that have a direct correlation with the economic output
and emission rate of the source (i.e., mass emitted per unit of activity).
(2)
Actual emissions--Shall equal the total emissions during
the selected time period, using the unit's actual daily operating hours, production
rates, and types of materials processed, stored, or combusted during the selected
time period.
(3)
Applicable emission point--The emission point that is either
generating an emission reduction or using a discrete emission credit.
(4)
Area source--Any source included in the agency emissions
inventory under the area source category.
(5)
Baseline--Emissions that occur prior to an emission reduction
strategy, considering all limitations required by applicable state and federal
regulations. The baseline may not exceed the most recent level of emissions
reported in the emissions inventory used for state implementation plan (SIP)
determinations. For reduction strategies that exceed 12 months, the baseline
is established after the first year of generation and is fixed for the life
of the strategy. A new baseline is established for each emission reduction
strategy.
(6)
Baseline activity--The source's actual level of activity
based on the unit's actual daily operating hours, production rates, or types
of materials processed, stored, or combusted averaged over any consecutive
two calendar year period including and following the most recent year of emissions
inventory used for SIP determinations or subsequent year(s) which precede
the emission reduction strategy or credit use period. For sources in existence
less than two years, a shorter time period not less than 12 months may be
considered by the executive director.
(7)
Baseline emission rate--The source's rate of emissions
per unit of activity during the baseline activity period.
(8)
Baseline emissions--The source's total actual emissions
based on the baseline activity and baseline emission rate.
(9)
Certified--Any emission reduction that is determined to
be creditable upon review and approval by the executive director.
(10)
Curtailment--A temporary or partial reduction in activity
level at any facility or mobile source.
(11)
Discrete emission credit--An emission reduction generated
over a discrete period of time, and measured in tons. A creditable emission
credit such as a discrete emission reduction credit (DERC) or mobile discrete
emission reduction credit (MDERC).
(12)
Discrete emission reduction credit (DERC)--A creditable
emission reduction which is created during a generation period, quantified
after the period in which emissions reductions are made, and expressed in
tons.
(13)
Emission reduction--An actual reduction of emissions from
a stationary or mobile source.
(14)
Emission reduction strategy--The method implemented to
reduce the source's emissions beyond that required by state or federal law,
regulation, or agreed order.
(15)
Generation period--The discrete period of time, not exceeding
12 months, over which a DERC is created.
(16)
Generator--The owner or operator of a source that creates
an emission reduction.
(17)
Level of activity--The amount of activity at a source
measured in terms of production, fuel use, raw materials input, or other similar
units that have a direct correlation with the economic output and emission
rate of the source (i.e., mass emitted per unit of activity).
(18)
Mobile discrete emission reduction credit (MDERC or discrete
mobile credit)--A credit that is surplus, generated by a mobile source strategy.
It is a creditable emission reduction that is created during a generation
period, quantified after the period in which emissions reductions are made,
and expressed in tons.
(19)
Mobile emissions baseline--Mobile emissions that occur
prior to a mobile emission reduction strategy, considering all limitations
required by applicable state and federal regulations. A valid mobile emission
baseline can be calculated by either using measured emissions of an appropriately
sized sample of the participating mobile sources using an approved United
States Environmental Protection Agency (EPA) test procedure or by using estimated
emissions of the participating mobile sources using the most recent edition
of EPA's on-road or non-road mobile emissions factor models, or other model
as applicable. To ensure that mobile credits are surplus, mobile source baseline
emissions estimates for each year of the proposed mobile source control program
must be the same as, or lower than, those used, or proposed to be used, in
the SIP in which the control program is proposed.
(20)
Mobile source--On-road (highway) vehicles (e.g., automobiles,
trucks, and motorcycles) and non- road vehicles (e.g., trains, airplanes,
agricultural equipments, industrial equipment, construction vehicles, off-road
motorcycles, and marine vessels).
(21)
Mobile source baseline activity--The mobile source's level
of activity during the applicable mobile source baseline year.
(22)
Mobile source baseline emissions--The mobile source's
total emissions based on the product of mobile source baseline activity and
mobile source baseline emission rate.
(23)
Most stringent allowable emissions rate--The emissions
rate of a source, considering all limitations required by applicable local,
state, and federal regulations.
(24)
Ozone season--The portion of the year when ozone monitoring
is federally required to occur in a specific geographic area.
(25)
Permanent--An emission reduction that is long-lasting
and unchanging for the remaining life of the source.
(26)
Protocol--A replicable and workable method of estimating
emission rates or activity levels used to calculate the amount of emission
reduction generated or credits required for stationary or mobile sources.
(27)
Quantifiable--An emission reduction that can be measured
or estimated with confidence using replicable techniques.
(28)
Real reduction--A reduction in which actual emissions
are reduced.
(29)
Source--As defined in §101.1 of this title (relating
to Definitions).
(30)
Shutdown--The permanent cessation of an activity producing
emissions at a facility.
(31)
Strategy activity--The source's level of activity during
the DERC generation period.
(32)
Strategy emission rate--The source's level of activity
during the DERC generation period.
(33)
Surplus--An emission reduction that is not otherwise required
of a source by a state or federal law, regulation, or agreed order.
(34)
Use period--The period of time over which the user source
applies discrete emission credits to an applicable emission reduction requirement.
(35)
User--The owner or operator of a source that acquires
and uses discrete emission credits to meet a regulatory requirement, demonstrate
compliance, or offset an emission increase.
(36)
Use strategy--The compliance requirement for which discrete
emission credits are being used.
§101.372.General Provisions
(a)
Applicable pollutants. Reductions of volatile organic compounds
(VOCs), nitrogen oxides (NO
x
), carbon (CO),
sulfur dioxide (SO
2
), and particulates with an
aerodynamic diameter of less than or equal to a nominal ten microns (PM
(b)
Discrete emission credit requirements.
(1)
Discrete emission reduction credit (DERC)--To be creditable
as a DERC, an emission reduction must be real, quantifiable, and surplus at
the time the discrete emission credit is generated. The creditable reduction
must have occurred after the most recent year of emissions inventory used
for state implementation plan (SIP) determinations for all applicable pollutants
and the source's annual emissions prior to the discrete emission credit application
must have been reported or represented in the emissions inventory used for
SIP determinations.
(2)
Mobile discrete emission reduction credit (MDERC)--To be
creditable as an MDERC, an emission reduction must be quantifiable, real,
and surplus. The discrete emission credit must be surplus at the time it is
created, as well as when it is used. The creditable reduction must have occurred
after the most recent year of emissions inventory used for SIP determinations
for all applicable pollutants, the mobile source's emissions must have been
represented in the emissions inventory used for SIP determinations, and the
mobile sources are in the attainment demonstration baseline. If a mobile reduction
is implemented that is not in the baseline for emissions, this would not constitute
an emission reduction.
(3)
Emission reductions from a source which are certified as
discrete emission credits under this division cannot be recertified in whole
or in part as emission credits under another division within this subchapter.
(c)
Eligible sources include the following:
(1)
stationary sources (including area sources);
(2)
mobile sources; or
(3)
any stationary source (including area sources) or mobile
source associated with actions by federal agencies under §101.30 of this
title (relating to Conformity of General Federal Actions to State Implementation
Plans).
(d)
Life of a discrete emission credit. A discrete emission
credit is available for use after the notice of generation, DC-1 Form, has
been received and deemed creditable by the commission registry in accordance
with subsection (h) of this section, and may be used anytime thereafter.
(e)
Geographic scope. Emission reductions generated in the
State of Texas may be creditable and used in the state with the following
limitations.
(1)
VOC and NO
x
discrete emission
credits generated in an ozone attainment area may be used in any county or
portion of a county designated as attainment or unclassified, but may not
be used in an ozone nonattainment area.
(2)
VOC and NO
x
discrete emission
credits generated in an ozone nonattainment area may be used either in the
same ozone nonattainment area in which they were generated, or in any county
or portion of a county designated as attainment or unclassified.
(3)
VOC and NO
x
discrete emission
credits generated in an ozone nonattainment area may not be used in any other
ozone nonattainment area, except as provided in this subsection.
(4)
CO, SO
2
, and PM
10
discrete emission credits must be used in the same metropolitan
statistical area in which the reduction was generated.
(5)
VOC and NO
x
discrete emission
credits generated in other counties, states, or nations can be used in any
attainment or nonattainment county provided a demonstration has been made
and approved by the executive director and the EPA to show that the emission
reductions achieved in the other county, state, or nation improves the air
quality in the county where the credit is being used.
(f)
Trading discontinuation. The trading of discrete emission
credits may be discontinued by the executive director in whole or in part
and in any manner, with commission approval, as a remedy for problems resulting
from trading in a localized area of concern.
(g)
Ozone season. In areas having an ozone season of less than
12 months, VOC and NO
x
discrete emission credits
generated outside the ozone season may not be used during the ozone season.
(h)
The registry. All required notices of discrete emission
credit generators and users must be submitted to the registry. A notice submitted
by a generator or user will be reviewed for credibility and when deemed certified,
posted to the registry. The registry will assign a unique number to each ton
of emission reductions generated. The registry will maintain current listings
of all credits available or used for each ozone nonattainment area. One combined
listing for all the counties or portions of counties designated as attainment
or unclassified will be provided by the registry.
(i)
Recordkeeping. The generator must maintain a copy of all
notices and backup information submitted to the registry for a minimum of
five years, following the completion of the generation period. The user must
maintain a copy of all notices and backup information submitted to the registry
for a minimum of five years, following the completion of the use period. Other
relevant reference material or raw data must also be maintained on-site by
the participating sources. The user must also maintain a copy of the generator's
notice and backup information for a minimum of five years after the use is
completed. The records shall include, but not necessarily be limited to:
(1)
the name, emission point number (EPN), and facility identification
number (FIN) of each unit using discrete emission credits;
(2)
the amount of discrete emission credits being used by each
unit;
(3)
the specific number, name, or other identification of discrete
emission credits used for each unit.
(j)
Public information. All information submitted with a notice
or report regarding the nature and quantity of emissions associated with the
use or generation of discrete emission credits is public information and may
not be submitted as confidential. Any claim of confidentiality for this type
of material or failure to submit all information may result in the rejection
of the emission reduction. All non-confidential notices and information regarding
the generation, use, and availability of discrete emission credits may be
obtained from the registry.
(k)
Authorization to emit. A discrete emission credit created
under this division is a limited authorization to emit the specified pollutants
in accordance with the provisions of this section, the Federal Clean Air Act,
and the Texas Clean Air Act, as well as regulations promulgated thereunder.
A discrete emission credit does not constitute a property right. Nothing in
this division should be construed to limit the authority of the commission
or the United States Environmental Protection Agency to terminate or limit
such authorization.
(l)
Program participation. The executive director has the authority
to prohibit a company from participating in discrete emission credit trading
either as a generator or user, if the executive director determines that the
company has violated the requirements of the program or abused the privileges
provided by the program.
§101.373.Protocols.
(a)
All discrete emission credit source categories must use
an United States Environmental Protection Agency (EPA) approved protocol if
one exists for the applicable source. If the source wants to deviate from
an EPA approved protocol, EPA approval is required before the protocol can
be used.
(b)
If an EPA approved protocol does not exist, the amount
of discrete emission credits in tons will be determined and certified based
on actual monitoring results, when available, or otherwise calculated using
good engineering practices, including calculation methodologies in general
use in new source review (NSR) permitting. The source must collect relevant
data sufficient to characterize the process emissions of the affected pollutant
and the process activity level for all representative phases of source operation
during the period under which discrete emission credits are created or used.
(c)
Discrete emission credit generation.
(1)
Discrete emission reduction credits (DERCs) may be generated
by any strategy that reduces a source's emission rate below its baseline and
is approved by the executive director, except for the following:
(A)
temporary curtailment of an activity at a source;
(B)
modification or discontinuation of any activity that is
otherwise in violation of a federal, state, or local law;
(C)
emissions reductions required to comply with any provision
under Title I of the Federal Clean Air Act (FCAA) regarding tropospheric
ozone, or Title IV of the FCAA regarding acid rain;
(D)
emission reductions of hazardous air pollutants, as defined
in the FCAA, §112, from application of a standard promulgated under FCAA, §112;
(E)
emission reductions which have occurred as a result of
transferring the emissions to another source;
(F)
emission reductions credited or used under any other emissions
trading program;
(G)
emission reductions occurring at a source which received
an alternative emission limitation to meet a state reasonably available control
technology requirement, except to the extent that the emissions are reduced
below the level that would have been required had the alternative emission
limitation not been issued; and
(H)
emission reductions at a facility with a flexible permit,
unless the reductions are made permanent and enforceable or the generator
can demonstrate that the emission reductions were not used to satisfy the
conditions for the facilities under the flexible permit.
(2)
A mobile discrete emission reduction credit (MDERC) may
be generated by any mobile source emission reduction strategy that creates
actual mobile source emission reductions under this rule, and is subject to
the approval of the commission.
(d)
Discrete emission credits generation calculation.
(1)
DERCs, except for shutdowns, are calculated as follows.
Figure: 30 TAC §101.373(d)(1)
(A)
The amount of DERCs generated must be rounded down to the
nearest ton.
(B)
For shutdown emission reduction strategies, the quantity
of emission reduction generated is equivalent to the baseline emissions.
(C)
The generation period for a shutdown is five years. Shutdown
DERCs must be generated and noticed to the registry on an annual basis.
(D)
If a source's emissions exceed its allowable emission limit,
the amount of emissions exceeding the limit may not be certified as DERCs.
(2)
An MDERC may be calculated from the annual difference between
the mobile source emissions baseline and the actual emissions level after
the MDERC strategy has been put in place. The MDERC must be based on actual
in-use emissions of the replacement or substitute mobile source. Emission
baselines for quantifying MDERCs should include the following information
and data as appropriate, but not be limited to:
(A)
the emission standard to which the mobile source is subject
or emission performance to which the mobile source is certified;
(B)
the measured in-use emissions levels per unit of use from
all significant mobile source emissions sources;
(C)
the number of mobile sources in the participating group;
(D)
the type or types of mobile sources by model year; and
(E)
the actual activity level, hours of operation or miles
traveled by type, and model year.
(e)
Registration and certification.
(1)
A notice of generation and generator certification (DEC-1
Form), must be submitted to the executive director no later than 90 days after
the discrete emission reduction strategy activity has been completed, or no
later than 90 days after the completion of the first 12 months of generation,
if the generation period exceeds 12 months, whichever is sooner. Submission
of the DEC-1 Form should continue every 12 months thereafter for each subsequent
year of generation.
(2)
In the notice for a stationary source, including area source,
the generator must include the following information for each pollutant reduced
at each applicable emission point:
(A)
the name, address, county, telephone number, contact person,
permit or standard exemption numbers, account number of the generator, and
the unique facility identification number (FIN) and emission point number
(EPN) of the applicable emission points;
(B)
the name of the owner and/or operator of the generator
source;
(C)
the generation period;
(D)
a complete description of the generation activity;
(E)
for shutdown emission reduction strategies, an explanation
as to whether production shifted from the shut down facility to another facility
in the same nonattainment area;
(F)
the amount of emission credits generated;
(G)
for volatile organic compound (VOC) reductions, a list
of the specific compounds reduced;
(H)
the baseline emission activity, baseline emission rate,
emission reduction strategy emission rate, emission reduction strategy activity,
emissions inventory data from the most recent year of emissions inventory
used for state implementation plan determinations and emissions inventory
data for the two consecutive years used to determine the baseline activity
for each applicable pollutant and emission point;
(I)
the most stringent emission rate for the applicable emission
point, considering all the local, state, and federal applicable regulatory
requirements;
(J)
a complete description of the protocol used to calculate
the emission reduction generated;
(K)
the actual calculations performed by the generator to determine
the amount of discrete emission credits generated; and
(L)
a statement that the emission reductions on which the emission
credits DERCs are based are real, surplus, and not based on an emission reduction
strategy that is prohibited.
(3)
The notice for a mobile source generator must include the
following information to verify the credit calculation, but is not limited
to:
(A)
the name, address, county, telephone number, and contact
person;
(B)
the name of the owner and/or operator of the generator
source;
(C)
the date of the reduction;
(D)
a complete description of the generation activity;
(E)
the amount of discrete mobile source emission credits generated;
(F)
the mobile source baseline emission activity, mobile source
baseline emission rate, mobile source baseline total emissions, and the mobile
source strategy;
(G)
a complete description of the protocol used to calculate
the discrete mobile source emission reduction generated;
(H)
the actual calculations performed by the generator to determine
the amount of discrete mobile source emission credits generated; and
(I)
a statement that the discrete mobile source emission reductions
on which the MDERCs are based are real, surplus, and not based on a mobile
source emission reduction strategy that is prohibited.
(4)
Registrations will be reviewed in order to determine the
credibility of the reductions. Reductions determined to be creditable will
be certified by the executive director.
(5)
The applicant will be notified in writing if the executive
director denies the notification. The applicant may submit a revised notification
at any time.
(f)
Discrete emission credit practices.
(1)
The amount of DERCs, in tons, will be determined and certified
based on actual monitoring results, when available, or otherwise calculated
using good engineering practices, including calculation methodologies in general
use in NSR permitting. The source must collect relevant data sufficient to
characterize the process emissions of the affected pollutant and the process
activity level for all representative phases of source operation during the
period under which DERCs are created or used.
(2)
The amount of MDERCs will be quantified in tons. MDERCs
will be determined and certified based on: EPA methodologies, when available;
actual monitoring results, when available; otherwise calculated using the
most current EPA MOBILE model; or otherwise calculated using creditable emission
reduction measurement or estimation methodologies which satisfactorily address
the analytical uncertainties of mobile source emissions reduction strategies.
The generator must collect relevant data sufficient to characterize the process
emissions of the affected pollutant and the process activity level for all
representative phases of source operation during the period under which the
MDERCs are created or used.
(3)
All discrete emission credits are deposited in the registry
and reported as available credits until they are used, withdrawn, or expire.
(4)
Compliance burden and enforcement.
(A)
The generator is responsible for assuring that the discrete
emission credits generated are certified.
(B)
The user is responsible for ensuring that discrete emission
credits which currently reside in the registry and are not certified are certified
prior to use.
(5)
Discrete emission credits may be used if the following
requirements are met.
(A)
The user must have ownership of a sufficient amount of
discrete emission credits before the use period for which the specific discrete
emission credits are to be used.
(B)
The user must hold sufficient discrete emission credits
to cover the user's compliance obligation at all times.
(C)
The user shall acquire additional discrete emission credits
during the use period if the user determines that he does not possess enough
discrete emission credits to cover the entire use period. The user must acquire
additional credits as allowed under this section prior to the shortfall, or
the user will be in violation of this section.
(D)
Source operators may acquire and use only discrete emission
credits listed on the registry.
(6)
With the exception of uses prohibited in paragraph (7)
of this subsection or strictly prohibited in other rules or regulations, discrete
emission credits may be used to meet or demonstrate compliance with any mobile
or stationary regulatory requirement including the following:
(A)
to exceed any allowable emission level, if the following
conditions are met:
(i)
in ozone nonattainment areas, permitted facilities may
use discrete emission credits to exceed permit allowables by no more than
25 tons for nitrogen oxides (NO
x
) or five tons
for VOC in a 12-month period as approved by the executive director. This use
is limited to one exceedance up to 12 months, within any 24-month period per
use strategy. The use must extend beyond a 24-hour period; or
(ii)
at permitted facilities in counties or portions of counties
designated as attainment or unclassified, discrete emission credits may be
used to exceed permit allowables by values not to exceed the prevention of
significant deterioration significance levels as provided in 40 Code of Federal
Regulations, §52.21(b)(23), as approved by the executive director prior
to use. This use is limited to one exceedance up to 12 months, within any
24-month period per use strategy. The user must demonstrate that there will
be no adverse impacts from the use of discrete emission credits at the levels
requested;
(B)
as NSR offsets if the following requirements are met:
(i)
the user must obtain the executive director's approval
prior to the use of specific discrete emission credits to cover, at a minimum,
one year of operation of the new or modified source in the NSR permit;
(ii)
the NSR permit must contain an enforceable requirement
that the source obtain at least one additional year of offsets before continuing
operation in each subsequent year;
(C)
compliance with NO
x
cap and
trade requirements as provided in §101.356(d)of this title (relating
to Allowance Banking and Trading).
(D)
compliance with §115.950 of this title (relating to
Emissions Trading) and §117.570 of this title (relating to Use of Emission
Credits for Compliance), as allowed.
(7)
A discrete emission credit, under this division, may not
be used:
(A)
before it has been acquired by the user;
(B)
for netting to avoid the applicability of federal and state
NSR requirements;
(C)
to meet FCAA requirements for:
(i)
new source performance standards under FCAA, §111;
(ii)
lowest achievable emission rate standards under FCAA, §173(a)(2);
(iii)
best available control technology standards under FCAA, §165(a)(4);
(iv)
hazardous air pollutants standards under FCAA, §112,
including the requirements for maximum achievable control technology;
(v)
standards for solid waste combustion under FCAA, §129;
(vi)
requirements for a vehicle inspection and maintenance
program under FCAA, §182(b)(4) or (c)(3);
(vii)
ozone control standards set under FCAA, §183(e)
and (f);
(viii)
clean-fueled vehicle requirements under FCAA, §246;
(ix)
motor vehicle emissions standards under FCAA, §202;
(x)
standards for nonroad vehicles under FCAA, §213;
(xi)
requirements for reformulated gasoline under FCAA, §211(k);
or
(xii)
requirements for Reid vapor pressure standards under
FCAA, §211(h) and (i).
(D)
to allow an emissions increase of an air contaminant that
exceeds the limitations of §106.261(3) or (4) or §106.262(3) of
this title (relating to Facilities (Emission Limitations) and Facilities
(Emission and Distance Limitations)) except as approved by the executive director;
(E)
to authorize a source whose emissions are enforceably limited
to below applicable major source threshold levels, as defined in §122.10
of this title (relating to General Definitions), to operate with actual emissions
above those levels without triggering applicable requirements that would otherwise
be triggered by such major source status;
(F)
to exceed an allowable emission level where the exceedance
would cause or contribute to a condition of air pollution as determined by
the executive director.
(8)
Calculation of discrete emission credits.
(A)
A user may use the following equation to calculate the
amount of discrete emission credits necessary to comply with §117.223
of this title (relating to Source Cap) instead of the equations in §117.223(b)(1)
and (2) of this title.
Figure: 30 TAC §101.373(f)(8)(A)
(B)
Otherwise, the amount of discrete emission credits needed
to demonstrate compliance or meet a regulatory requirement is calculated as
follows.
Figure: 30 TAC §101.373(f)(8)(B)
(C)
The amount of discrete emission credits needed must be
rounded up to the nearest ton.
(D)
The user must possess 10% more discrete emission credits
than are needed, as calculated in subparagraph (B) of this paragraph, to ensure
that the source's environmental contribution retirement obligation will be
met.
(E)
If the amount of discrete emission credits needed to meet
a regulatory requirement or to demonstrate compliance is greater than ten
tons, an additional 5.0% of the discrete emission credits needed, as calculated
in subparagraph (B) of this paragraph, must be acquired to ensure that sufficient
discrete emission credits are available to the user with an adequate compliance
margin.
(F)
The amount of discrete emission credits needed for NSR
offsets equals the quantity of tons needed to achieve the maximum allowable
emission level set in the user's NSR permit. The user must also purchase and
retire enough discrete emission credits to meet the offset ratio requirement
in the user's ozone nonattainment area. The user must purchase and retire
either the environmental contribution of 10% or the offset ratio, whichever
is higher.
(G)
Discrete emission credits that are not used during the
use period are surplus and remain available for transfer or use by the holder.
In addition, any portion of the calculated environmental contribution not
attributed to actual use is also available.
(g)
Notice of intent to use. A notice of intent to use, DEC-2
Form, must be submitted to the executive director in accordance with the following
requirements:
(1)
discrete emission credits may be used only after the user
has submitted the notice to the registry;
(2)
the notice must be submitted at least 45 days prior to
the first day of the use period if the generator is a stationary source, and
90 days if the generator is a mobile source, and every 12 months thereafter
for each subsequent year if the use period exceeds 12 months;
(3)
a copy of the notice must also be sent to the federal land
manager 30 days prior to use if the user is located within 100 kilometers
of a Class I area;
(4)
the notice for a stationary or area source user must include
the following information for each use:
(A)
the name, address, county, telephone number, contact person,
permit or standard exemption numbers, and account number of the user, and
the unique FIN and EPN identification numbers for each emission point;
(B)
the name of the owner and/or operator of the user source;
(C)
the applicable state and federal requirements that the
discrete emission credits will be used to comply with and the intended use
period;
(D)
the amount of discrete emission credits needed;
(E)
the baseline emission rate, activity level, and total emissions
for the applicable emission points;
(F)
the actual emission rate, activity level, and total emissions
for the applicable emission points;
(G)
the most stringent emission rate and the most stringent
emission level for the applicable emission points, considering all applicable
regulatory requirements;
(H)
a complete description of the protocol used to calculate
the amount of discrete emission credits needed;
(I)
the actual calculations performed by the user to determine
the amount discrete emission credits needed;
(J)
the date on which the discrete emission credits were acquired
or will be acquired;
(K)
the discrete emission credit generator and the serial numbers
of the discrete emission credits acquired or to be acquired;
(L)
the price of the discrete emission credits acquired or
the expected price of the discrete emission credits to be acquired; and
(M)
a statement that due diligence was taken to verify that
the discrete emission credits were not previously used, that the discrete
emission credits were not generated as a result of actions prohibited under
this regulation, and that the discrete emission credits will not be used in
a manner prohibited under this regulation.
(5)
the notice for a mobile source user must include the following
information:
(A)
the name, address, county, telephone number, and contact
person;
(B)
the name of the owner and/or operator of the user source;
(C)
the applicable state and federal requirements that the
discrete emission credits will be used to comply with and the intended use
period;
(D)
the amount of discrete emission credits needed;
(E)
the mobile source baseline emission rate, mobile source
activity level, and total mobile source emissions for the applicable mobile
sources;
(F)
the actual mobile source emission rate, activity level,
and total emissions for the applicable mobile source;
(G)
the most stringent mobile source emission rate and the
most stringent mobile source emission level for the applicable emission points,
considering all applicable regulatory requirements;
(H)
a complete description of the protocol used to calculate
the amount of MDERCs needed;
(I)
the actual calculations performed by the user to determine
the amount MDERCs needed;
(J)
the date on which the MDERCs were acquired or will be acquired;
(K)
the MDERC generator and the serial numbers of the MDERCs
acquired or to be acquired;
(L)
the price of the MDERCs acquired or the expected price
of the MDERCs to be acquired;
(M)
a statement that due diligence was taken to verify that
the MDERCs DERCs were not previously used, that the MDERCs were not generated
as a result of actions prohibited under this regulation, and that the MDERCs
will not be used in a manner prohibited under this regulation; and
(N)
a certification of use, which must contain certification
under penalty of law by a responsible official of the user source of truth,
accuracy, and completeness. This certification must state that based on information
and belief formed after reasonable inquiry, the statements and information
in the document are true, accurate, and complete;
(6)
a user may submit a notice late in the case of an emergency,
but the notice must be submitted before the discrete emission credits can
be used. The user must include a complete description of the emergency situation
in the notice of intent to use. All other notices submitted less than 45 days
prior, or 90 days prior for a mobile source, to use will be considered late
and in violation;
(7)
the user is responsible for determining the credits it
will purchase and notifying the executive director of the selected generating
source in the notice of intent to use. If the generator's credits are rejected
or the notice of generation is incomplete, the use of discrete emission credits
by the user may be delayed by the executive director. The user cannot use
any discrete emission credits that have not been certified by the executive
director. The executive director may reject the use of discrete emission credits
by a source if the credit and use cannot be demonstrated to meet the requirements
of this section.
(A)
Actual discrete emission credits use.
(i)
The user shall calculate:
(I)
the amount of discrete emission credits used, including
the amount of discrete emission credits retired to cover the environmental
contribution associated with actual use; and
(II)
the amount of discrete emission credits not used, including
the amount of excess discrete emission credits that were purchased to cover
the environmental contribution but not associated with the actual use, and
available for future use.
(ii)
A report of use, DEC-3 Form, must be submitted to the
registry in accordance with the following requirements:
(I)
a report of use must be submitted within 90 days after
the end of the use period;
(II)
the report must be submitted within 90 days of the conclusion
of each 12-month use period, if applicable;
(III)
the report is to be used as the mechanism to update or
amend the notice of intent to use and must include any information different
from that reported in the notice of intent to use, including, but not limited
to, the following items:
(-a-)
purchase price of the discrete emission credits obtained
prior to the current use period;
(-b-)
the actual amount of discrete emission credits possessed
during the use period;
(-c-)
the actual emissions during the use period for VOC and
NO
x
;
(-d-)
the actual amount of discrete emission credits used;
(-e-)
the actual environmental contribution; and
(-f-)
the amount of discrete emission credits available for
future use.
(iii)
The user is in violation of this section if the user
submits the report of use later than the allowed 90 days following the conclusion
of the use period.
(iv)
The registry shall not contain proprietary information.
(B)
Compliance burden and enforcement.
(i)
The user is responsible for assuring that a sufficient
quantity of discrete emission credits is acquired to cover the applicable
source's emissions for the entire use period. The user should ensure that
the credits are real, surplus, and properly quantified discrete emission credits
for purchase.
(ii)
The user is in violation of this section if the user does
not possess enough discrete emission credits to cover the credit need for
the use period. If the user possesses an insufficient quantity of discrete
emission credits to cover its compliance need, the user will be out of compliance
for the entire use period, unless the user can demonstrate otherwise. Each
day the user is out of compliance may be considered a violation.
(iii)
Users may not transfer their compliance burden and legal
responsibilities to a third party participant. Third party participants may
only act in an advisory capacity to the user.
(C)
Discrete emission credits are freely transferable in whole
or in part, and may be traded or sold to a new owner anytime before the expiration
date of the discrete emission credit. The Emissions Banking and Trading Program
must be notified by means of an DC-4 Form prior to the transfer. The executive
director will issue a letter to the discrete emission credit purchaser reflecting
the discrete emission credits purchased by the new owner, and a letter to
the discrete emission credit seller showing any remaining discrete emission
credits available to the original owner. Discrete emission credits may be
transferrable only after the executive director grants approval of the transaction.
§101.374.Program Audits.
(a)
No later than three years after the effective date of this
division section, and every three years thereafter, the executive director
will audit this program.
(b)
The audit will evaluate the timing of credit generation
and use, the impact of the program on the state's attainment demonstration
and the emissions of hazardous air pollutants, the availability and cost of
credits, compliance by the participants, and any other elements the executive
director may choose to include.
(c)
The executive director will recommend measures to remedy
any problems identified in the audit. The trading of discrete emission credits
may be discontinued by the executive director in part or in whole and in any
manner, with commission approval, as a remedy for problems identified in the
program audit.
(d)
The audit data and results will be completed and submitted
to the United States Environmental Protection Agency and made available for
public inspection within six months after the audit begins.
This agency hereby certifies that the adoption has been reviewed
by legal counsel and found to be a valid exercise of the agency's legal authority.
Filed
with the Office of the Secretary of State on December 29, 2000
TRD-200009074
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Effective date: January 18, 2001
Proposal publication date: August 25, 2000
For further information, please call: (512) 239-6087
The Texas Natural Resource Conservation Commission (commission) adopts
amendments to §114.6, Low Emission Fuel Definitions; §114.312, Low
Emission Diesel Standards; §114.313, Designated Alternate Limits; §114.314,
Registration of Diesel Producers and Importers; §114.315, Approved Test
Methods; §114.316, Monitoring, Recordkeeping, and Reporting Requirements; §114.317,
Exemptions to Low Emission Diesel Requirements; and §114.319, Affected
Counties and Compliance Dates. The commission adopts these amendments to Chapter
114, Control of Air Pollution From Motor Vehicles, and corresponding revisions
to the state implementation plan (SIP) in order to control ground-level ozone
in the Houston/Galveston (HGA), Dallas/Fort Worth (DFW), and Beaumont/Port
Arthur (BPA) ozone nonattainment areas. Sections 114.6, 114.312, 114.313,
114.315, 114.316, 114.317, and 114.319 are adopted
with changes
to the proposed text as published in the August 25, 2000
issue of the
Texas Register
(25 TexReg 8169).
Section 114.314 is adopted
without changes
to the proposed text and will not be republished.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE ADOPTED RULES
The HGA ozone nonattainment area is classified as Severe-17 under the Federal
Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401
et seq.), and therefore is required to attain the one-hour ozone standard
of 0.12 parts per million (ppm) by November 15, 2007. In addition, 42 USC, §7502(a)(2),
requires attainment as expeditiously as practicable, and 42 USC, §7511a(d),
requires states to submit ozone attainment demonstration SIPs for severe ozone
nonattainment areas such as HGA. The HGA area, defined by Brazoria, Chambers,
Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has
been working to develop a demonstration of attainment in accordance with 42
USC, §7410. On January 4, 1995, the state submitted the first of its
Post-1996 SIP revisions for HGA.
The January 1995 SIP consisted of urban airshed model (UAM) modeling for
1988 and 1990 base-case episodes, proposed rules to achieve a 9% rate-of-progress
(ROP) reduction in volatile organic compounds (VOC), and a commitment schedule
for the remaining ROP and attainment demonstration elements. At the same time,
but in a separate action, the State of Texas filed for the temporary nitrogen
oxide (NO
x
) waiver allowed by 42 USC, §7511a(f).
The January 1995 SIP and the NO
x
waiver were
based on early base-case episodes which marginally exhibited model performance
in accordance with the United States Environmental Protection Agency (EPA)
modeling performance standards, but which had a limited data set as inputs
to the model. In 1993 and 1994, the commission was engaged in an intensive
data-gathering exercise known as the COAST study. The state believed that
the enhanced emissions inventory, expanded ambient air quality and meteorological
monitoring, and other elements would provide a more robust data set for modeling
and other analysis, which would lead to modeling results that the commission
could use to better understand the nature of the ozone air quality problem
in the HGA area.
Around the same time as the 1995 submittal, the EPA policy regarding SIP
elements and timelines went through changes. Two national programs in particular
resulted in changing deadlines and requirements. The first of these programs
was the Ozone Transport Assessment Group (OTAG). This group grew out of a
March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for
Air and Radiation, that allowed states to postpone completion of their attainment
demonstrations until an assessment of the role of transported ozone and precursors
had been completed for the eastern half of the nation, including the eastern
portion of Texas. Texas participated in this study, and it has been concluded
that Texas does not significantly contribute to ozone exceedances in the Northeastern
United States. The other major national initiative that has impacted the SIP
planning process is the revisions to the national ambient air quality standard
(NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing
the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996,
concurrent with the proposal of the standards, the EPA proposed an interim
implementation plan (IIP) that it believed would help areas like HGA transition
from the old to the new standard. In an attempt to avoid a significant delay
in planning activities, Texas began to follow this guidance, and readjusted
its modeling and SIP development timelines accordingly. When the new standard
was published, the EPA decided not to publish the IIP, and instead stated
that, for areas currently exceeding the one-hour ozone standard, that standard
would continue to apply until it is attained. The FCAA requires that HGA attain
the standard by November 15, 2007.
The EPA issued revised draft guidance for areas such as HGA that do not
attain the one-hour ozone standard. The commission adopted on May 6, 1998
and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained
the following elements in response to the EPA guidance: UAM modeling based
on emissions projected from a 1993 baseline out to the 2007 attainment date;
an estimate of the level of VOC and NO
x
reductions
necessary to achieve the one-hour ozone standard by 2007; a list of control
strategies that the state could implement to attain the one-hour ozone standard;
a schedule for completing the other required elements of the attainment demonstration;
a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the
EPA believed made the previous version of that SIP unapprovable; and evidence
that all measures and regulations required by Subpart 2 of Title I of the
FCAA to control ozone and its precursors have been adopted and implemented,
or are on an expeditious schedule to be adopted and implemented.
In November 1998, the SIP revision submitted to the EPA in May 1998 became
complete by operation of law. However, the EPA stated that it could not approve
the SIP until specific control strategies were modeled in the attainment demonstration.
The EPA specified a submittal date of November 15, 1999 for this modeling.
In a letter to the EPA dated January 5, 1999, the state committed to model
two strategies showing attainment.
As the HGA modeling protocol evolved, the state eventually selected and
modeled seven basic modeling scenarios. As part of this process, a group of
HGA stakeholders worked closely with commission staff to identify local control
strategies for the modeling. Some of the scenarios for which the stakeholders
requested evaluation included options such as California-type fuel and vehicle
programs as well as an acceleration simulation mode equivalent motor vehicle
inspection and maintenance program. Other scenarios incorporated the estimated
reductions in emissions that were expected to be achieved throughout the modeling
domain as a result of the implementation of several voluntary and mandatory
state-wide programs proposed or planned independently of the SIP. It should
be made clear that the commission did not propose that any of these strategies
be included in the ultimate control strategy submitted to the EPA in 2000.
The need for and effectiveness of any controls which may be implemented outside
the HGA eight-county area will be evaluated on a county-by-county basis.
The SIP revision was adopted by the commission on October 27, 1999, submitted
to the EPA by November 15, 1999, and contained the following elements: photochemical
modeling of potential specific control strategies for attainment of the one-hour
ozone standard in the HGA area by the attainment date of November 15, 2007;
an analysis of seven specific modeling scenarios reflecting various combinations
of federal, state, and local controls in HGA (additional scenarios H1 and
H2 build upon Scenario VIf); identification of the level of reductions of
VOC and NO
x
necessary to attain the one-hour
ozone standard by 2007; a 2007 mobile source budget for transportation conformity;
identification of specific source categories which, if controlled, could result
in sufficient VOC and/or NO
x
reductions to attain
the standard; a schedule committing to submit by April 2000 an enforceable
commitment to conduct a mid-course review; and a schedule committing to submit
modeling and adopted rules in support of the attainment demonstration by December
2000.
The April 19, 2000 SIP revision for HGA contained the following enforceable
commitments by the state: to quantify the shortfall of NO
x
reductions needed for attainment; to list and quantify potential
control measures to meet the shortfall of NO
x
reductions needed for attainment; to adopt the majority of the necessary rules
for the HGA attainment demonstration by December 31, 2000, and to adopt the
rest of the shortfall rules as expeditiously as practical, but no later than
July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform
a mid-course review by May 1, 2004; and to perform modeling of mobile source
emissions using the EPA mobile source emissions model (MOBILE6), to revise
the on-road mobile source budget as needed, and to submit the revised budget
within 24 months of the model's release. In addition, if a conformity analysis
is to be performed between 12 months and 24 months after the MOBILE6 release,
the state will revise the motor vehicle emissions budget (MVEB) so that the
conformity analysis and the SIP MVEB are calculated on the same basis.
In order for the state to have an approvable attainment demonstration,
the EPA indicated that the state must adopt those strategies modeled in the
November submittal and then adopt sufficient controls to close the remaining
gap in NO
x
emissions. The modeling and other
analysis supporting these rules and the HGA SIP indicate a gap of approximately
an additional 91 tons per day (tpd) of NO
x
reductions
is necessary for an approvable attainment demonstration. The predicted emission
reductions is necessary to successfully demonstrate attainment.
The emission reduction requirements included as part of this SIP revision
represent substantial, intensive efforts on the part of stakeholder coalitions
in the HGA area. These coalitions, involving local governmental entities,
elected officials, environmental groups, industry, consultants, and the public,
as well as the commission and the EPA, have worked diligently to identify
and quantify potential control strategy measures for the HGA attainment demonstration.
Local officials from the HGA area have formally submitted a resolution to
the commission, requesting the inclusion of many specific emission reduction
strategies.
This rule adoption is one element of the control strategy for the HGA SIP.
Adoption and implementation of this control strategy is necessary in order
for the HGA nonattainment area to comply with the requirements of the FCAA
and achieve attainment for ozone. Additional elements of the control strategy
for the HGA SIP are being adopted concurrently in this issue of the
The amount of NO
x
reductions required for
the area to attain the ozone NAAQS has been estimated by extensive use of
sophisticated air quality grid modeling, which because of its scientific and
statutory grounding, is the chief policy tool for designing emission reduction
strategies. The FCAA, 42 USC, §7511a(c)(2), requires the use of photochemical
grid modeling for ozone nonattainment areas designated serious, severe, or
extreme. The modeling has been conducted with input from a technical oversight
committee. Commission staff have continued to improve the air quality modeling
technology and refine emission inventory data. Numerous emission control strategies
were considered in developing the modeling. Varying degrees of reductions
from point sources, on-road and non-road mobile sources, and area sources
were analyzed in multiple iterations of modeling, to test the effectiveness
of different NO
x
reductions. The attainment demonstration
modeling and other analysis submitted for public hearing and comment concurrently
with the HGA SIP show that a significant amount of NO
x
reductions practicably achievable are necessary from ozone control
strategies in order for the HGA nonattainment area to achieve the ozone NAAQS
by 2007, including reductions from surrounding counties included in the HGA
consolidated metropolitan statistical area (CMSA).
Additionally, reductions associated from the ozone control strategies that
will be implemented outside the HGA nonattainment area will benefit the HGA
nonattainment area. This is due to the regional nature of air pollution, the
contribution from mobile sources, and the economies of scale and associated
market advantages related to distribution networks for some strategies. At
the time the 1990 FCAA Amendments were enacted, the focus on controlling ozone
pollution was centered on local controls. However, for many years an ever
increasing number of air quality professionals have concluded that ozone is
a regional problem requiring regional strategies in addition to local control
programs. As nonattainment areas across the United States prepared attainment
demonstration SIPs in response to the 1990 FCAA Amendments, several areas
found that modeling attainment was made much more difficult, if not impossible,
due to high ozone and ozone precursor levels entering from the boundaries
of their respective modeling domains, commonly called transport. Recent science
indicates that regional approaches may provide improved control of ozone air
pollution.
The current SIP revision contains rules, enforceable commitments, photochemical
modeling analyses, and calculation of the remaining NO
x
reductions required to reach attainment (gap calculation) in support
of the HGA ozone attainment demonstration. In addition, this SIP contains
Post-1999 ROP plans for the milestone years 2002 and 2005, and for the attainment
year 2007. The SIP also contains enforceable commitments to implement further
measures, if needed, in support of the HGA attainment demonstration, as well
as a commitment to perform and submit a mid-course review.
The HGA ozone nonattainment area will need to ultimately reduce NO
These rules are one element of the control strategy for the HGA Attainment
Demonstration SIP. The purpose of these rules is to establish a LED air pollution
control strategy that reduces NO
x
emissions necessary
for the HGA nonattainment area to be able to demonstrate attainment with the
ozone NAAQS. Additional benefits will be achieved in the BPA, El Paso, and
DFW ozone nonattainment areas, the 95-county central and eastern Texas region,
as well as the remainder of the state.
The adopted revisions to the LED rules will require LED fuel statewide
for on-road use. In addition, the revisions to the LED rules will require
LED fuel for both on-road and non-road use in the eight counties in the HGA
ozone nonattainment area which includes Brazoria, Chambers, Fort Bend, Galveston,
Harris, Liberty, Montgomery, and Waller Counties; the four counties of the
DFW ozone nonattainment area which includes Collin, Dallas, Denton, and Tarrant
Counties; the three counties of the BPA ozone nonattainment area which includes
Hardin, Jefferson, and Orange Counties; and 95 additional central and eastern
Texas counties including Anderson, Angelina, Aransas, Atascosa, Austin, Bastrop,
Bee, Bell, Bexar, Bosque, Bowie, Brazos, Burleson, Caldwell, Calhoun, Camp,
Cass, Cherokee, Colorado, Comal, Cooke, Coryell, De Witt, Delta, Ellis, Falls,
Fannin, Fayette, Franklin, Freestone, Goliad, Gonzales, Grayson, Gregg, Grimes,
Guadalupe, Harrison, Hays, Henderson, Hill, Hood, Hopkins, Houston, Hunt,
Jackson, Jasper, Johnson, Karnes, Kaufman, Lamar, Lavaca, Lee, Leon, Limestone,
Live Oak, Madison, Marion, Matagorda, McLennan, Milam, Morris, Nacogdoches,
Navarro, Newton, Nueces, Panola, Parker, Polk, Rains, Red River, Refugio,
Robertson, Rockwall, Rusk, Sabine, San Jacinto, San Patricio, San Augustine,
Shelby, Smith, Somervell, Titus, Travis, Trinity, Tyler, Upshur, Van Zandt,
Victoria, Walker, Washington, Wharton, Williamson, Wilson, Wise, and Wood
Counties.
The commission's current understanding, based upon national studies as
well as the commission's own studies, is that ozone must be controlled at
two levels: the regional level and the urban level. Historically, the FCAA
has states focusing on the ozone problem at the local level. Recently, however,
this has begun to change. The EPA has started to incorporate the findings
of the OTAG, the Southern Oxidant Study, and the advice of stakeholders (e.g.,
the Federal Advisory Committee Act Subcommittee on Ozone, Particulate Matter,
and Regional Haze Implementation) into recent policy guidance, encouraging
states to factor regional reductions into their control plans.
On a national level, the OTAG study and its findings are particularly noteworthy.
OTAG was established by the EPA to work with states in the eastern portion
of the country to develop strategies to address the regional ozone problem.
Among the OTAG determinations were that ozone is pervasive; ozone and the
compounds that form it are transported both at lower levels of the atmosphere
and aloft from one day to the next; and ozone precursors reductions over a
large area are beneficial in the lowering of regional ozone background levels.
The commission's own studies provided evidence that there is regional transport
of ozone and ozone precursors in Texas, and that regional reductions of ozone
precursors are beneficial. The commission's own modeling studies have shown
that pollutant sources across Texas contribute to regional ozone background
levels, and that regional ozone precursor reductions will lower those background
levels. These studies and upper air monitoring have found that regional air
pollution should be considered when studying air quality in the Texas ozone
nonattainment areas. This work is supported by the OTAG study which is the
most comprehensive attempt ever undertaken to understand and quantify the
transport of ozone. Both the commission and OTAG study results point to the
need to take a regional approach to control air pollutants, such as that described
in the regional control strategy adopted by the commission.
Reducing regional background ozone levels through a regional strategy will
serve three purposes. It will give existing nonattainment areas the flexibility
to design optimal local control strategies to help them attain the one-hour
and eight-hour ozone standards. It will help areas, which are currently close
to violating the standards, to avoid actually violating. Finally, over the
longer term, it will help prevent the developing areas of the state from ever
violating the standards.
The regional aspect of the state LED fuel program was developed to provide
LED fuel for use in areas of the state that could potentially have a negative
air quality impact on current ozone nonattainment areas, near nonattainment
areas, and future areas of concern. For example, the HGA ozone nonattainment
area currently needs every possible emission reduction to demonstrate attainment;
the BPA nonattainment area attainment goals are heavily influenced by transport
from HGA; the DFW ozone nonattainment area is also impacted by transport and
has little leeway to handle additional emissions based on their current attainment
demonstration modeling; and several near-nonattainment areas for the new eight-hour
standard are seeking immediate reductions to preclude a nonattainment area
designation. All of these areas will benefit from the reductions attributed
to the regional aspect of the state-wide LED fuel program.
The main attractiveness of the fuel-based strategy is that it has a more
immediate impact than other controls. Once the fuel is in the marketplace,
it begins having an immediate air quality impact as both old and new vehicles
and non-road equipment begin using the new fuel.
A state-wide LED fuel requirement facilitates distribution. The state-wide
coverage area for on-road use will create a large enough market to ease the
costs of distribution. Supplies can be co-mingled in the pipeline, trading
can take place, and tracking compliance will be simplified. Because a federal
reformulated gasoline is already distributed to the DFW and HGA ozone nonattainment
areas, and the state's low-Reid vapor pressure (RVP) gasoline is already distributed
to the 95-county central and eastern Texas regional area, diesel producers
and importers will be able to use the current distribution system to distribute
state LED fuel to the affected areas beginning in 2006 when the sulfur content
in LED is limited to 15 ppm for the HGA, BPA, and DFW ozone nonattainment
areas and the 95-county central and eastern Texas region.
A state-wide LED fuel requirement also reduces non-compliant fuel usage
within the nonattainment areas due to out-of-area refueling by pass-through
truck traffic. According to data shown on a 1997 truck traffic flow map published
by the Texas Department of Transportation (TxDOT), over 10,000 trucks per
day traverse the HGA nonattainment area. In addition, according to a TxDOT
report,
Effect of the North American Free Trade Agreement
on the Texas Highway System,
December 1998, the volume of truck traffic
through the HGA nonattainment area directly associated with the North American
Free Trade Agreement ranges between 1,001 and 2,500 trucks per day. Therefore,
state-wide coverage for on-road LED use will ensure that higher volumes of
pass-through truck traffic will be refueling with LED within the state, and
will be using this fuel when traveling within the state's nonattainment areas.
The LED fuel will lower the emissions of NO
x
and other pollutants from fuel combustion. Because NO
x
is a precursor to ground-level ozone formation, reduced emissions
of NO
x
will result in ground-level ozone reductions.
To comply with the state LED regulations, diesel fuel producers and importers
must ensure that diesel fuel distributed to the LED fuel zone meets the specifications
stated in these adopted rules. These rules require that, beginning May 1,
2002, diesel fuel produced for delivery and ultimate sale to the consumer
in the affected area shall not exceed 500 ppm sulfur, must contain less than
10% by volume of aromatic hydrocarbons, and must have a cetane number of 48
or greater. In addition, these rules will require the sulfur content in the
diesel fuel supplied to the DFW, BPA, and HGA ozone nonattainment areas and
95 central and eastern Texas counties, be reduced to 15 ppm sulfur beginning
June 1, 2006. Also, these rules require diesel fuel producers and importers
who provide fuel to the affected areas to register with the commission and
provide quarterly status reports.
These rules will also revise definitions that will impact who is affected
by the adopted state LED fuel program as well as who is impacted by the current
requirements of the regional low-RVP gasoline program, specified in §§114.301,
114.304 - 114.307, and 114.309. These rules will restrict the registration,
reporting, and testing requirements of these programs to those persons who
have direct control over changes in fuel content, i.e., those persons who
produce fuel or import fuel into the state.
The commission is aware that the EPA is currently proposing revised nationwide
diesel fuel sulfur controls. If a new federal diesel fuel sulfur rule is adopted
that covers the areas in Texas impacted by this rule, and the federal rule
is at least as stringent as these rules, then the commission may consider
compliance with the national rule equally effective and may repeal the state
sulfur requirements for diesel fuel.
The commission is expanding the LED fuel ozone control strategy which was
developed for the DFW area and requiring diesel fuel content limits more restrictive
than federal diesel fuel regulations. The current federal regulations governing
diesel fuel quality in Title 40 Code of Federal Regulations (40 CFR) Part
80, Regulation of Fuels and Fuel Additives, §80.29, Controls and Prohibitions
on Diesel Fuel Quality, establish limits for fuel content for diesel fuel
used in on-road motor vehicle applications. These federal regulations limit
sulfur in on-road diesel fuel to 500 ppm and allow the producer to choose
between meeting a minimum cetane number of 40 or a maximum aromatic hydrocarbon
content of 35% by volume. The state's LED regulations limit on-road diesel
to 500 ppm sulfur, 10% aromatic hydrocarbons, and a 48 cetane minimum, and
with a more restrictive limit on sulfur being implemented on-road and non-road
in the HGA, DFW, BPA ozone nonattainment areas and 95 central and eastern
Texas counties in June 2006. As such, the commission is submitting, as part
of the SIP, concurrent with this rulemaking, a request for a waiver in accordance
with the 42 USC, §7545(C)(4)(c), for the on-road portion of these rules.
Although the EPA regulates diesel fuel content for on-road use, it does not
regulate the fuel content for non-road diesel fuel. Therefore, because there
is currently no federal limit on the content of non-road diesel, the state
has independent authority to place controls on the composition of non-road
diesel fuel and the commission does not believe that a waiver is needed for
the non-road portion of these rules. This adopted SIP submittal is available
to the public by contacting Heather Evans at (512) 239-1970.
Modeling performed for the commission assessing the benefits of this NO
The commission developed this NO
x
emission
control strategy to cover the eight counties contained in the HGA ozone nonattainment
area. The coverage area also includes all counties in the state for on-road
diesel fuel use; and the four DFW ozone nonattainment counties, the three
BPA ozone nonattainment counties, as well as 95 central and eastern Texas
counties for both on-road and non-road diesel fuel use. The involvement of
the statewide and regional counties as part of the NO
x
emission control strategy is necessary for the HGA and DFW areas
to demonstrate attainment of the ozone NAAQS. These rules are intended to
help bring the ozone nonattainment areas into compliance and to help keep
attainment and near nonattainment areas from going into nonattainment by reducing
emissions in those areas and by reducing transport of emissions into those
areas. The state-wide and regional coverage will also provide a greater market
for diesel fuel producers and importers to provide the fuel required by these
regulations and avoid a patchwork of multiple requirements within the state.
Additionally, the state-wide and regional coverage should help alleviate concerns
regarding out-of-area refueling practices by making it difficult to refuel
outside the covered area for use within a nonattainment or near nonattainment
area.
The commission is open to considering future substitution of this measure
if a federal program is completed and achieves substantially equivalent emission
reductions. In addition, the commission is open to future agreements with
entities for emission reductions from other fuel-related strategies. In order
for agreements to be used, the commission may have to revisit these rules
and the SIP to enable agreements to be considered for substitution of these
rules.
The commission solicited comment regarding the possible benefits of reducing
sulfur content to 15 ppm prior to the 2006 federal deadline as a possible
alternative to controls on aromatics and cetane as proposed. There were two
comments received which are addressed in the ANALYSIS OF TESTIMONY section
of this preamble.
The commission also solicited comment on additional flexibilities relating
to rule content and implementation which have not been addressed in this or
other concurrent rulemakings. These flexibilities may be available for both
mobile and stationary sources. Additional flexibilities may also be achieved
through innovative and/or emerging technology which may become available in
the future. Additional sources of funds for incentive programs may become
available to substitute for some of the measures considered here. There were
two comments received which are addressed in the ANALYSIS OF TESTIMONY section
of this preamble.
SECTION BY SECTION DISCUSSION
The adopted amendments to §114.6 contain revisions to the following
definitions: bulk plant, imported, import facility, importer, produce, and
production facility. The amendment to the definition of bulk plant is needed
for clarification of the definition and will insert the word "fuel" that was
inadvertently left out of the original rulemaking. The phrase "solely by truck"
is also amended to "by truck or pipeline" to account for those bulk plants
that have pipeline delivery. These amendments to the definitions of imported,
import facility, and importer are necessary to clarify that only those persons,
except persons acting as common carriers, who import fuel into the state are
covered by these definitions. These amendments will impact who is affected
by the current requirements of the regional RVP gasoline program, specified
in §§114.301, 114.304 - 114.307, and 114.309, as well as the amendments
to the LED fuel program and will restrict the registration, reporting, and
testing requirements of these programs to those persons who have direct control
over changes in fuel content, i.e., those persons who produce fuel or import
fuel into the state. The amendments to definitions of produce and production
facility are necessary for clarification of these terms upon the repeal of
the definitions of refiner and refinery. In addition, the amendments to §114.6
contain new definitions for common carrier, motor vehicle, and non-road equipment.
The amendments to §114.6 also repealed the definitions of refiner and
refinery. These definitions were repealed as being redundant with the terminology
already being used for producer and production facility. Also, as a result
of the new definitions, the other existing definitions are to be renumbered
accordingly.
These amendments to §114.312 revise subsection (b) to modify the sulfur
content standard for diesel fuel to provide for the phase down of sulfur content
in certain affected areas from 500 ppm to 15 ppm. Subsection (b)(2) was deleted
and subsection (b)(3) was renumbered in order to be consistent with anticipated
federal rulemaking. The deadline for meeting 15 ppm sulfur has been changed
from May to June to match the deadline proposed in the federal sulfur regulations.
Subsection (b) has also been revised to clarify that 15 ppm fuel is not required
until the compliance date identified in §114.319. The amendments to §114.312
also revise subsection (e) to provide clarifying changes to replace the terms,
"refiner" and "refiner's refinery" with the term, "producer" and "production
facility," as newly defined in §114.6. In addition, the amendments to §114.312
revise subsection (g) to provide reference to the testing methods prescribed
in the adopted amendments to §114.315 and to change the reference prescribing
which requirements may be satisfied by subsection (g) from subsection (a)
to subsections (c) and (d) which was the original intent at proposal.
The amendments to §114.313 clarify the language of subsection (c)
by adding commas in two locations.
The amendments to §114.314 clarify language by adding the word "fuel"
after the phrase "low emission diesel (LED)." The amendments also change the
word "chapter" to "division" to clarify that LED producers and importers shall
comply with the requirements of the subchapter division regarding LED.
The amendments to §114.315 revise subsection (a) to establish the
American Society for Testing and Materials (ASTM) Test Method D287-92(1995)
as the approved test method for determining the American Petroleum Institute
(API) gravity, ASTM Test Method D445-97 as the approved test method for determining
viscosity, ASTM Test Method D93-99c as the approved test method for determining
the flash point, and ASTM Test Method D86-00 as the approved test method for
determining the distillation temperatures of the diesel fuel. The amendments
to §114.315 also contain a new subsection (c) which establishes the test
procedures and approval process for obtaining the executive director's approval
of an alternative diesel fuel formulation, and a new subsection (d) which
establishes the approval process for alternative diesel fuel formulations
which are intended only for use in non-road equipment.
The amendments to §114.316 revise subsection (e) to require the California
Air Resources Board (CARB) executive order number, or the approval notification
number as issued by the executive director, to be included on the product
transfer documents if the diesel fuel being transferred complies with one
of those alternatives.
The amendments to §114.317 contain a new subsection (a) which establishes
an exemption from the requirements of these rules for diesel fuel used for
research, development, or testing purposes; new subsection (b) establishes
an exemption for diesel fuel used for racing purposes; new subsection (c)
exempts the owner or operator of a retail fuel dispensing outlet from all
monitoring, recordkeeping, and reporting requirements of the rule, except
for the requirement to maintain product transfer documents; the previous subsection
(b) is renumbered to subsection (d); the language of subsection (d) is revised
to provide an exemption that stipulates diesel fuel not meeting the LED requirements
is not prohibited in the affected counties as long as it is not ultimately
used to power a diesel fueled compression-ignition engine in a motor vehicle
or non-road equipment in the affected counties, except for that fuel used
in conjunction with research, development, or testing purposes, or as competition
racing fuel. These exemptions were added to more closely match federal motor
fuel regulations and are not expected to have a significant impact on air
quality.
The amendments to §114.319 contain a new subsection (a) which establishes
the compliance date for statewide coverage of the LED program for on-road
diesel fuel use, a new subsection (b) which establishes the compliance date
and coverage area for the use of LED for both on-road and non-road use, and
a new subsection (c) which establishes the compliance date and coverage area
for the sulfur content phase down to 15 ppm sulfur. Subsection (a) has also
been revised to clarify that some requirements of §114.312 will not be
applicable statewide. Finally, the proposed new subsection (c) which would
have established a compliance date of May 1, 2004 and coverage area for the
sulfur content to phase down to 30 ppm sulfur has been deleted in order to
be consistent with anticipated federal rulemaking, and the proposed new subsection
(d) has been renumbered to (c).
FINAL REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the rulemaking action in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225, and has determined
that the rulemaking meets the definition of a "major environmental rule" as
defined in that statute. "Major environmental rule" means a rule, the specific
intent of which is to protect the environment or reduce risks to human health
from environmental exposure and that may adversely affect in a material way
the economy, a sector of the economy, productivity, competition, jobs, the
environment, or the public health and safety of the state or a sector of the
state. The amendments to Chapter 114 are intended to protect the environment
or reduce risks to human health from environmental exposure to ozone and could
affect in a material way, a sector of the economy, competition, and the environment
due to its impact on the fuel manufacturing and distribution network of the
state. The amendments are intended to implement an LED air pollution control
program as part of the strategy to reduce emissions of NO
x
necessary for the counties included in the HGA ozone nonattainment
area to be able to demonstrate attainment with the ozone NAAQS.
These adopted rules do not meet any of the four applicability criteria
for requiring a regulatory analysis of "major environmental rule" as defined
in the Texas Government Code. Section 2001.0225 applies only to a major environmental
rule the result of which is to: 1) exceed a standard set by federal law, unless
the rule is specifically required by state law; 2) exceed an express requirement
of state law, unless the rule is specifically required by federal law; 3)
exceed a requirement of a delegation agreement or contract between the state
and an agency or representative of the federal government to implement a state
and federal program; or 4) adopt a rule solely under the general powers of
the agency instead of under a specific state law.
As discussed earlier in this preamble, this rule adoption is one element
of the control strategy for the HGA SIP. Adoption and implementation of this
control strategy is necessary in order for the HGA nonattainment area to comply
with the requirements of the FCAA and achieve attainment for ozone. Additional
elements of the control strategy for the HGA SIP are being adopted concurrently
in this issue of the
Texas Register,
or were
included in the HGA SIP considered by the commission on December 6, 2000,
and planned to be submitted to EPA by December 31, 2000.
The amendments are intended to implement an LED air pollution control program
as part of the strategy to reduce emissions of NO
x
necessary for the counties included in the HGA ozone nonattainment area to
be able to demonstrate attainment with the ozone NAAQS. Specifically, the
LED fuel requirements within these rules were developed in order to meet the
ozone NAAQS set by the EPA under 42 USC, §7409, and therefore meet a
federal requirement. This is based on the analysis provided in the rule proposal
preamble which was published in the August 25, 2000 issue of the
Texas Register,
including the discussion in the Public Benefit and
Costs section.
These rules do not exceed an express standard set by federal law, since
they implement requirements of the FCAA. Provisions of 42 USC, §7410,
require states to adopt a SIP which provides for "implementation, maintenance,
and enforcement" of the primary NAAQS in each air quality control region of
the state. These rules were specifically developed as part of an overall control
strategy to meet the ozone NAAQS set by the EPA under 42 USC, §7409.
While §7410 does not require specific programs, methods, or reductions
in order to meet the standard, state SIPs must include "enforceable emission
limitations and other control measures, means or techniques (including economic
incentives such as fees, marketable permits, and auctions of emissions rights),
as well as schedules and timetables for compliance as may be necessary or
appropriate to meet the applicable requirements of this chapter," (meaning
42 USC, Chapter 85, Air Pollution Prevention and Control). It is true that
42 USC does require some specific measures for SIP purposes, like the inspection
and maintenance program, but those programs are the exception, not the rule,
in the SIP structure of FCAA. The provisions of the FCAA recognize that states
are in the best position to determine what programs and controls are necessary
or appropriate in order to meet the NAAQS. This flexibility allows states,
affected industry, and the public, to collaborate on the best methods for
attaining the NAAQS for the specific regions in the state. Even though the
FCAA allows states to develop their own programs, this flexibility does not
relieve a state from developing a program that meets the requirements of §7410.
In order to avoid federal sanctions, states are not free to ignore the requirements
of §7410 and must develop programs to assure that the nonattainment areas
of the state will be brought into attainment on schedule. Thus, while specific
measures are not prescribed, both a plan and emission reductions are required
to assure that the nonattainment areas of the state will be able to meet the
attainment deadlines set by the FCAA. The EPA has provided the criteria for
both the submission and evaluation of attainment demonstrations developed
by states to comply with the FCAA. This criteria requires states to provide,
in addition to other information, photochemical modeling and an analysis of
specific emission reduction strategies necessary to attain the NAAQS. The
commissions photochemical modeling and other analysis indicate that substantial
emission reductions from both mobile and point source categories are necessary
in order to demonstrate attainment. In this case, this rulemaking is intended
to achieve reductions in ozone precursor emissions in the HGA nonattainment
area. Specifically, as noted elsewhere in this rule preamble, the emission
reductions associated with these rules are a necessary element of the attainment
demonstration required by the FCAA.
In addition, 42 USC, §7502(a)(2), requires attainment as expeditiously
as practicable, and 42 USC, §7511a(d), requires states to submit ozone
attainment demonstration SIPs for severe ozone nonattainment areas such as
HGA. By policy, the EPA requires photochemical grid modeling to demonstrate
whether the 42 USC, §7511a(f), NO
x
measures
would contribute to ozone attainment. The commission has performed photochemical
grid modeling which predicts that NO
x
emission
reductions, such as those required by these rules, will result in reductions
in ozone formation in the HGA ozone nonattainment area and help bring HGA
into compliance with the air quality standards established under federal law
as NAAQS for ozone. The 42 USC, §7511a(f), exemption from NO
x
measures for HGA expired on December 31, 1997. The expiration of
the exemption under 42 USC, §7511a(f), was based on the finding that
NO
x
reductions in HGA are necessary for attainment
of the ozone standard. Therefore, the adopted amendments are necessary components
of and consistent with the ozone attainment demonstration SIP for HGA, required
by 42 USC, §7410.
During the 75th Legislative Session, Senate Bill (SB) 633 amended the Texas
Government Code to require agencies to perform a regulatory impact analysis
(RIA) of certain rules. The intent of SB 633 was to require agencies to conduct
an RIA of extraordinary rules. With the understanding that this requirement
would seldom apply, the commission provided a cost estimate for SB 633 that
concluded "based on an assessment of rules adopted by the agency in the past,
it is not anticipated that the bill will have significant fiscal implications
for the agency due to its limited application." The commission also noted
that the number of rules that would require assessment under the provisions
of the bill was not large. This conclusion was based, in part, on the criteria
set forth in the bill that exempted adopted rules from the full analysis unless
the rule was a major environmental rule that exceeds a federal law. As previously
discussed, 42 USC does not require specific programs, methods, or reductions
in order to meet the NAAQS; thus, states must develop programs for each nonattainment
area to ensure that area will meet the attainment deadlines. Because of the
ongoing need to address nonattainment issues, the commission routinely proposes
and adopts SIP rules. The legislature is presumed to understand this federal
scheme. If each rule adopted for inclusion in the SIP was considered to be
a major environmental rule that exceeds federal law, then every SIP rule would
require the full RIA contemplated by SB 633. This conclusion is inconsistent
with the conclusions reached by the commission in its cost estimate and by
the Legislative Budget Board (LBB) in its fiscal notes. Because the legislature
is presumed to understand the fiscal impacts of the bills it passes, and that
presumption is based on information provided by state agencies and the LBB,
the commission believes that the intent of SB 633 was only to require the
full RIA for rules that are extraordinary in nature. While the SIP rules will
have a broad impact, that impact is no greater than is necessary or appropriate
to meet the requirements of the FCAA. The commission has consistently applied
this construction to its rules since this statute was enacted in 1997. Since
that time, the legislature has revised the Texas Government Code but left
this provision substantially unamended. It is presumed that "when an agency
interpretation is in effect at the time the legislature amends the laws without
making substantial change in the statute, the legislature is deemed to have
accepted the agency's interpretation."
Central Power &
Light Co. v. Sharp,
919 S.W.2d 485. 489 (Tex. App. Austin 1995),
The commission's interpretation of the RIA requirements is also supported
by a change made to the Texas Administrative Procedure Act (APA) by the legislature
in 1999. In an attempt to limit the number of rule challenges based upon APA
requirements, the legislature clarified that state agencies are required to
meet these sections of the APA against the standard of "substantial compliance."
Texas Government Code, §2001.035. The legislature specifically identified
Texas Government Code, §2001.0225 as falling under this standard. The
commission has substantially complied with the requirements of §2001.0225.
Therefore, in addition to not exceeding an express standard set by federal
law, these rules do not exceed state requirements, and are not adopted solely
under the general powers of the agency because the provisions of the TCAA, §§382.011,
382.012, 382.017, 382.019, 382.037(g), and 382.039 authorize the commission
to implement a plan for the control of the states air quality, including measures
necessary to meet federal requirements. The remaining applicability criteria,
pertaining to exceeding a delegation agreement or contract between the state
and the federal government does not apply. Thus, the commission is not required
to conduct a regulatory analysis as provided in Texas Government Code, §2001.0225.
The commission solicited public comment on the draft RIA and received ten
comments. These comments are addressed in the ANALYSIS OF TESTIMONY section
of this preamble.
TAKINGS IMPACT ASSESSMENT
The commission evaluated this rulemaking action and performed an analysis
of whether the rules are subject to Texas Government Code, Chapter 2007. The
following is a summary of that analysis. The specific purpose of the rulemaking
action is to establish an LED fuel program which will act as an air pollution
control strategy to reduce NO
x
emissions necessary
for the eight counties included in the HGA ozone nonattainment area and other
nonattainment and near nonattainment areas of the state to be able to demonstrate
attainment with the ozone NAAQS.
Texas Government Code, §2007.003(b)(4), provides that Chapter 2007
does not apply to these rules since they are reasonably taken to fulfill an
obligation mandated by federal law. The rules fulfill federal mandates under
the 1990 Amendments to 42 USC, §7410. Specifically, the emission limitations
and control requirements within this rulemaking were developed in order to
meet the NAAQS for ozone set by the EPA under 42 USC, §7409. States are
primarily responsible for ensuring attainment and maintenance of NAAQS once
the EPA has established them. Under 42 USC, §7410, and related provisions,
states must submit, for approval by the EPA, SIPs that provide for the attainment
and maintenance of NAAQS through control programs directed to sources of the
pollutants involved. Therefore, the purpose of this rulemaking is to meet
the air quality standards established under federal law as NAAQS. Any NO
In addition, Texas Government Code, §2007.003(b)(13), states that
Chapter 2007 does not apply to an action that: 1) is taken in response to
a real and substantial threat to public health and safety; 2) is designed
to significantly advance the health and safety purpose; and 3) does not impose
a greater burden than is necessary to achieve the health and safety purpose.
This action is taken in response to the HGA and other areas of the state exceeding
the federal ambient air quality standard for ground-level ozone, which adversely
affects public health, primarily through irritation of the lungs. The action
significantly advances the health and safety purpose by reducing ozone levels
in HGA. Consequently, these rules meet the exemption in §2007.003(b)(13).
The commission has included elsewhere in this preamble its reasoned justification
for adopting this strategy and has explained why it is a necessary component
of the SIP which is federally mandated. This discussion, as well as the HGA
SIP which is being adopted concurrently, explains in detail that every rule
in the HGA SIP package is necessary and that none of the reductions in those
packages represent more than is necessary to bring the area into attainment
with the NAAQS. This rulemaking therefore meets the requirements of Texas
Government Code, §2007.003(b)(4) and (13). For these reasons the rules
do not constitute a takings under Chapter 2007 and do not require additional
analysis.
Comments received during the comment period regarding the TIA are addressed
in the ANALYSIS OF TESTIMONY section of this preamble.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that the rulemaking action relates to an action
or actions subject to the Texas Coastal Management Program (CMP) in accordance
with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources
Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter
281, Subchapter B, concerning Consistency with the CMP. As required by 30
TAC §281.45(a)(3) and 31 TAC §505.11(b)(2), relating to actions
and rules subject to the CMP, commission rules governing air pollutant emissions
must be consistent with the applicable goals and policies of the CMP. The
commission reviewed this action for consistency with the CMP goals and policies
in accordance with the rules of the Coastal Coordination Council, and determined
that the action is consistent with the applicable CMP goals and policies.
The CMP goal applicable to this rulemaking action is the goal to protect,
preserve, and enhance the diversity, quality, quantity, functions, and values
of coastal natural resource areas (31 TAC §501.12(1)). No new sources
of air contaminants will be authorized and NO
x
air emissions will be reduced as a result of these rules. The CMP policy applicable
to this rulemaking action is the policy that commission rules comply with
regulations in 40 CFR, to protect and enhance air quality in the coastal area
(31 TAC §501.14(q)). This rulemaking action complies with 40 CFR 51,
National Primary and Secondary Ambient Air Quality Standards, and with 40
CFR 52, Requirements for Preparation, Adoption, and Submittal of Implementation
Plans. Therefore, in compliance with 31 TAC §505.22(e), the commission
affirms that this rulemaking action is consistent with CMP goals and policies.
The commission solicited comments on the consistency of the proposed rules
with the CMP during the public comment period, and received no comments.
HEARINGS AND COMMENTERS
The commission held public hearings on this proposal at the following locations:
September 18, 2000, in Conroe and Lake Jackson; September 19, 2000 in Houston
(two hearings); September 20, 2000, in Katy and Pasadena; September 21, 2000,
in Beaumont, Amarillo, and Texas City; September 22, 2000, in Dayton, El Paso,
and Arlington; and September 25, 2000, in Austin and Corpus Christi. The comment
period closed at 5:00 p.m. on September 25, 2000.
The following commenters provided oral testimony and/or submitted written
testimony: AAE Technologies, Inc. (AAE); Ato Fina Petrochemicals (Ato Fina);
Air Surrey Natural Gas Vehicles, Inc. (Air Surrey); Alliance of Automobile
Manufacturers (Alliance); American Road and Transportation Builders Association
(ARTBA); Associated General Contractors of Texas (AGC-Texas); Association
of American Railroads (AAR); American Short Line and Regional Railroad Association
(ASLRRA); Baker Botts LLP (Baker Botts); British Petroleum-Amoco (BP); Business
Coalition for Cleaner Air (BCCA); CITGO Petroleum Corporation (CITGO); Canal
Barge Company, Inc. (CBC); City of Baytown (Baytown); City of Corpus Christi
(Corpus Christi); City of Fort Worth (Fort Worth); City of Lake Jackson (Lake
Jackson); City of Missouri City (Missouri City); Clean Diesel Technologies,
Inc. (CDTI); Corpus Christi Air Quality Committee (CCAQC); Corpus Christi
City Councilman Arnold Gonzales (Councilman Gonzales); Dow Chemical Company
(Dow); Dynegy, Inc. (Dynegy); Environmental Defense (ED); Ethyl Corporation
(Ethyl); ExxonMobil Corporation (ExxonMobil); Galveston-Houston Association
for Smog Prevention (GHASP); Grandparents of East Harris County (GEHC); Harris
County Judge Robert Eckels (Harris County); Houston Metropolitan Transit Authority
(Metro); Houston-Galveston Area Council (HGAC); Houston-Galveston Metropolitan
Planning Organization's Transportation Policy Council (Houston MPO); Intercoastal
Towing and Transportation Corporation (ITT); Kirby Inland Marine, Inc. (KIMI);
Koch Petroleum Group LP (Koch); League of Women Voters of Texas (LWV-TX);
Liberty County Sheriff Gregg Arthur (Liberty County Sheriff); Lyondell-CITGO
Refining Company, Ltd (Lyondell-CITGO); Manufacturers of Emission Controls
Association (MECA); RMT, Inc. on behalf of Montgomery County (Montgomery Co.);
Mothers for Clean Air (MCA); National Association of Truck Stop Operators
(NATSO); National Petrochemical and Refiners Association (NPRA); Paso del
Norte Clean Cities Coalition (Paso del Norte); Phillips 66 Company (Phillips
66); Port Industries of Corpus Christi (Port Industries); Port of Corpus Christi
Authority (PCCA); Texas Public Citizen (Public Citizen); Regional Air Quality
Consensus Group (RAQCG); Reliant Energy, Inc. (REI); Sierra Club, Galveston
Region (Sierra-Galveston); Sierra Club, Houston Regional Group (Sierra-Houston);
State Representative Jaime Capelo (Representative Capelo); State Representative
Vilma Luna (Representative Luna); State Senator Carlos F. Truan (Senator Truan);
Suderman and Young Towing Company, Inc. (Suderman); Texas Association of Business
and Chambers of Commerce (TABCC); Texas Citizens for a Sound Economy (TCSE);
Texas Department of Agriculture (TDA); Texas Motor Transportation Association
(TMTA); Texas Oil and Gas Association (TxOGA); Texas Petroleum Marketers and
Convenience Store Association (TPCA); Texas Waterway Operators Association
(TWOA); United States Department of Defense (DoD); EPA; Ultramar Diamond Shamrock
Corporation (UDS); Union Pacific Railroad Company (Union Pacific); Valero
Refining Company - Texas (Valero); Wesly Community Center (Wesly); Western
Towing Company (WTC); Willis Independent School District (WISD); and 57 individuals.
The following persons generally supported the proposal: AAE, Air Surrey,
Alliance, Baker Botts, BP, CDTI, CCAQC, Councilman Gonzales, DoD, ED, EPA,
Ethyl, Fort Worth, GEHC, GHASP, HGAC, Sierra-Houston, ITT, Lake Jackson, LWV-TX,
MECA, MCA, Public Citizen, Representative Capelo, Representative Luna, Senator
Truan, Houston MPO, Wesly, WISD, and 38 individuals.
The following persons generally opposed the proposal: ARTBA, Ato Fina,
AGC-Texas, AAR, ASLRRA, BCCA, CITGO, CBC, Baytown, Corpus Christi, Missouri
City, Dow, Dynegy, ExxonMobil, Sierra-Galveston, Harris County, KIMI, Koch,
Lyondell-CITGO, Liberty County Sheriff, Metro, Montgomery Co., NATSO, NPRA,
Phillips 66, Port Industries, PCCA, Paso del Norte, RAQCG, REI, Suderman,
TABCC, TCSE, TDA, TMTA, TPCA, TWOA, TxOGA, UDS, Union Pacific, Valero, WTC,
and 19 individuals.
The following persons suggested changes to the proposal as stated in the
ANALYSIS OF TESTIMONY section of this preamble: AAE, AAR, ASLRRA, AGC-Texas,
Air Surrey, ARTBA, Ato Fina, Baker Botts, Baytown, BCCA, BP, CBC, CITGO, Corpus
Christi, Houston MPO, DoD, Dow, Dynegy, EPA, Ethyl, ExxonMobil, Sierra-Galveston,
GEHC, GHASP, Harris County, HGAC, Sierra-Houston, KIMI, Koch, Lyondell-CITGO,
Liberty County Sheriff, MECA, Montgomery Co., NATSO, NPRA, Phillips 66, Port
Industries, PCCA, Paso del Norte, RAQCG, REI, Suderman, TABCC, TCSE, TDA,
TMTA, TPCA, TWOA, TxOGA, UDS, Union Pacific, Valero, WTC, and 15 individuals.
ANALYSIS OF TESTIMONY
AGC-Texas, Ato Fina, Baytown, BCCA, CITGO, Corpus Christi, Dow, Dynegy,
ExxonMobil, Harris County, Koch, Lyondell-CITGO, NATSO, NPRA, Phillips 66,
RAQCG, REI, TABCC, TxOGA, TPCA, UDS, Valero, and eight individuals expressed
opposition to all region-specific, patchwork, or boutique fuel control strategy
methods and requested that the commission refrain from implementing the proposed
rules. Instead, they supported and encouraged the adoption of new federal
diesel fuel regulations which are forthcoming in the near future. The new
federal regulations will provide virtually identical NO
x
emission reduction benefits at a much lower cost to the public. Koch
recommended that the commission withdraw this proposed rule and refrain from
seeking a waiver from EPA to regulate diesel in Texas. TxOGA commented that
the proposed federal low sulfur diesel fuels should supercede these proposed
rules if they are adopted by the commission. TxOGA strongly recommended that
the commission repeal all portions of these rules, including the rules regarding
aromatics and cetane, as soon as the federal rule is adopted.
The HGA ozone nonattainment area is required to have three years of emissions
monitoring data demonstrating compliance with the NAAQS to support the 2007
attainment demonstration. Therefore, implementing the LED standards in May
2002 provides the area the necessary time to allow the results of this control
strategy to be realized through ozone monitoring data. In addition, these
rules provide state requirements for non-road diesel fuel use which is not
currently addressed by federal regulation. The commission is also aware that
the EPA has issued a notice of proposed rulemaking (NPRM) for new heavy-duty
engine and vehicle emission standards and new diesel fuel standards. If the
outcome of this EPA proposal is a federal rule which covers the areas in Texas
impacted by these adopted rules, and the federal rule is at least as stringent
as any rules adopted as a result of this rulemaking, then the commission will
consider compliance with the national rule equally effective and may repeal
all or portions of the state requirements for diesel fuel. However, based
on the NPRM, it is quite likely that the EPA will only mandate sulfur reductions
for on-road use, leaving aromatics and cetane values at their current levels.
Because the EPA believes that the 2004 emission standards can be met without
recourse to NO
x
after-treatment devices, sulfur
reductions alone are not expected to generate further NO
x
reductions beyond the engine standards themselves. The commission
has made no change to the rule language in response to this comment.
NPRA commented that the United States House of Representatives Committee
on Science recently requested the United States Department of Energy (DOE),
Energy Information Administration (EIA) to conduct a study of the EPA proposed
15 ppm sulfur cap on highway diesel and that the EIA indicated that this study
will not be completed until April 2001, and therefore NPRA recommended that
the commission either withdraw the LED proposal or defer promulgation of this
proposal until after the commission has received and considered next year's
EIA report.
The commission believes that there is currently adequate information available
to support the adoption of these rules. The timeline deemed necessary by the
commission to allow fuel producers sufficient time to comply with these rules
and to allow the commission to meet SIP submission requirements has made adoption
of the rules necessary at this time. The commission has pledged to reconsider
all of it rules concerning the HGA attainment strategies during the mid-course
review in the 2003 to 2004 time frame. Since the 15 ppm sulfur requirement
does not begin until 2006 under these rules, the current timeline would allow
the commission to reconsider the rules in light of new information which may
be contained in the EIA report.
One individual commented that these proposed rules appear to be set up
to embarrass Texas and the Governor and that these proposed rules go far beyond
anything necessary to protect the environment. This individual further added
that the basis and analysis behind these proposed rules is flawed and should
be reevaluated.
The commission intent is not to embarrass Texas and the Governor, but instead
to comply with the timelines provided in 1990 FCAA amendments and subsequent
EPA guidance for submitting rules to demonstrate ozone attainment in HGA.
Accordingly, the commission has committed to adopting the majority of the
necessary rules for the HGA attainment demonstration by December 31, 2000.
As noted in the rule preamble, the purpose of these rules is to establish
an LED air pollution control strategy that reduces NO
x
emissions necessary for the HGA nonattainment area to be able to
demonstrate attainment with the ozone NAAQS. The science behind cleaner-burning
fuels is well established. The emission reductions anticipated by the implementation
of these rules are necessary to the success of the area in reaching attainment
and therefore the commission deemed it necessary for inclusion in the SIP.
As demonstrated in the SIP, the strategies do not require more reductions
than necessary to meet federal air quality standards.
NPRA recommended that implementation of new diesel fuel sulfur standards
should not occur before 2010. CITGO commented that reducing sulfur prior to
the introduction of the new heavy-duty engine vehicles, and to a level lower
than that required to enable technology, will provide minimal benefit in reducing
NO
x
and is certainly not cost effective.
The commission disagrees with this comment. Advanced diesel engine emission
control systems needed by the diesel engine manufacturers to comply with the
proposed 2007 federal heavy-duty diesel engine emission standards will require
ultra-low sulfur diesel fuel to operate efficiently. Therefore, the commission
is requiring reductions in diesel fuel sulfur beginning in June 2006. The
commission removed the requirement for 30 ppm sulfur in calendar year 2004
for the reasons specified in the SECTION BY SECTION DISCUSSION.
The Liberty County Sheriff expressed his concerns over who is going to
enforce these proposed regulations. One individual commented that the commission
needs to convey the strategies it plans to use to enforce these proposed rules
and that an efficient quality-assurance and enforcement program must be developed
and be part of the SIP document for reformulated liquid fuels to be a credible
component in the SIP.
As with all of its rules, the commission will enforce the requirements
after the rule compliance date and take appropriate action for noncompliance
situations, including situations in which a grandfathered source has modified
its operations without first obtaining the required permit authorization under
30 TAC Chapter 116 or Chapter 106. The rules are enforced by staff in the
commission's regional offices, as well as local air pollution control programs.
Local governments have the same power and are subject to the same restrictions
as the commission under TCAA, §382.015, Power to Enter Property, to inspect
the air and to enter public or private property in its territorial jurisdiction
to determine if the level of air contaminants in an area in its territorial
jurisdiction meet levels set by the commission. Local governments are not
required to enforce commission rules, but may sign cooperative agreements
with the commission to enforce the rules under TCAA, §382.115, Cooperative
Agreements. Local programs can also enforce commission rules without signing
a cooperative agreement. The authority of local governments to enforce air
pollution requirements is specified in detail in TCAA, §§382.111
- 382.115, and local governments can institute civil actions in the same manner
as the commission under Texas Water Code (TWC), §7.351.
The commission will work with local officials to ensure enforcement of
the SIP and SIP rules. The commission has existing relationships with pollution
control authorities in the City of Houston, Harris County, and Galveston County
for enforcement of other commission rules. The agency will continue enforcement
relationships with these entities and develop relationships with other local
officials as needed to create effective enforcement mechanisms for the SIP
and SIP rules.
The EPA commented that the commission should explain how the proposed rules
prohibit transport, supply, etc. of non-complying diesel fuel, and make any
person in the distribution system liable for such a violation.
The rules require all parties in the distribution chain to maintain copies
or records of product transfer documents for a minimum of two years. It is
clear in the rules that each party in the distribution chain is required to
comply with the rules, and, as with any rule, is subject to enforcement action
for a violation. As with all of its rules, the commission will enforce the
requirements after the compliance date and will take appropriate action for
noncompliance situations. The commission made no change to the rule language
in response to these comments.
HGAC and Sierra-Houston commented that the proposed rules should be implemented
statewide to provide adequate market and to maximize emission benefits for
the 2007 attainment data. Four individuals commented that the proposed rule
should be applied statewide. One individual commented that the proposed low-sulfur
diesel should be delayed until the federal mandate applies across the country
or it should be applied across the entire state since there is a high likelihood
of shortages due to refinery limitations. GHASP commented that the sulfur
concentration in all fuel be reduced to 15 ppm.
As noted in the rule preamble, the rules do apply statewide regarding the
requirement for the use of diesel fuel with 500 ppm maximum sulfur, 10% maximum
aromatics, and 48 minimum cetane, for on-road use in motor vehicles. In this
rulemaking, the commission cannot revise these proposed rules upon adoption
to apply the reductions of sulfur in 2006 for both on-road and non-road use
statewide or to other counties in Texas because the additional affected parties
would not have had adequate notice and opportunity to comment. Additionally,
requirements on any fuel but diesel is outside the scope of this rulemaking.
However, the commission will consider the need to expand the rules during
the mid-course review scheduled to be completed by May 1, 2004. The commission
made no change to the rule language in response to these comments.
HGAC commented that the commission should encourage introduction of cleaner
fuels nationally, including cleaner diesel fuel.
The commission provided comments to the EPA in support of the proposed
federal heavy-duty diesel engine standards and low sulfur diesel fuel rules.
Paso del Norte commented that studies conducted on improved diesel, so-called
clean diesel, have shown that improving diesel causes other problems, including
other types of cancers and other related health problems, that the commission
should analyze before adopting this proposal.
The commission disagrees with this comment. The differences between conventional
diesel fuel and the clean, or "reformulated," diesel fuel are that clean diesel
fuel contains less sulfur, less polycyclic aromatic compounds (PAC), and an
increase in cetane. The commission has conducted a literature search and has
not discovered any studies supporting the claim that the clean diesel causes
different types of cancers or other related health problems. However, the
literature does indicate that fuels with lower sulfur and PAC levels are potentially
less biologically hazardous. The commission is of the opinion that a clean
diesel formulation, such as the LED required by these rules, will reduce the
overall hazard potential. The commission made no change to the rule language
in response to this comment.
Koch commented that the commission should request the EPA to allow the
state to take credit in the SIP for reductions that will be achieved through
the implementation of the proposed federal heavy-duty diesel engine standards
and low sulfur diesel fuel program.
Because the EPA is still in the NPRM stage of this rulemaking process,
the commission cannot claim credit for this proposed initiative. In addition,
based on the NPRM, it is likely that the EPA will only mandate sulfur reductions,
leaving aromatics and cetane values at their current levels. Because the EPA
believes that the 2004 emission heavy-duty diesel emission standards can be
met without recourse to NO
x
after-treatment devices,
sulfur reductions alone are not expected to generate further NO
x
reductions beyond the engine standards themselves. With regard to
obtaining credit for "low emission diesel vehicles," the commission has modeled
the effects of heavy diesel vehicles meeting the 2004 emission standards,
and included these results in the 2007 emission projections. For these reasons
the commission believes the SIP modeling effort has already claimed the maximum
amount of NO
x
reduction credits available from
diesel vehicles and fuels, given the current federal rulemaking status.
Koch and TxOGA responded to the commission's request for comments regarding
the possible benefits of reducing sulfur to 15 ppm prior to the 2006 federal
deadline as a possible alternative to controls on aromatics and cetane by
commenting that Koch and TxOGA do not recommend the early implementation of
ultra-low sulfur diesel prior to the introduction of advanced technology engines
and catalysts that must utilize low sulfur diesel. Koch and TxOGA further
added that early introduction of ultra-low sulfur diesel fuel will not provide
the intended air quality benefits, nor will it make any difference in the
SIP accounting that is to take place in 2007.
The commission appreciates the response to our request for comments and
has revised the rule to delete the proposed requirements which would have
required 30 ppm sulfur by May 1, 2004 in order to provide greater flexibility
for producers to comply with these rules and to be consistent with anticipated
federal rulemaking.
Koch and TxOGA responded to the commission's request for comments regarding
additional flexibility relating to rule content and implementation. Commenters
indicated that the flexibility embodied in the proposed federal diesel rule
that allows adequate time to make changes to their refineries to reduce sulfur
levels is an excellent example of allowing industry to reasonably comply with
the rule and to smooth supply transitions for cleaner burning fuels. The flexibility
allowed by the federal rule is the critical reason Koch and TxOGA opposed
the proposed rules and supported the federal proposal for the HGA area.
The commission appreciates the response to our request for comments and
has taken these comments into consideration.
BCCA and TxOGA expressed opposition to the waiver request being submitted
to the EPA by the commission in accordance with 42 USC, §7545(c)(4)(C)
to implement the on-road portion of the proposed rules and expressed support
for the proposed federal low sulfur diesel rules.
The commission contends that the waiver request is necessary for implementation
of the on-road portion of the rules and that the rules will provide greater
emission reduction benefits than the proposed federal low sulfur diesel rules
from the reduction in aromatic content and an increase in cetane level. Therefore,
the commission is requesting this waiver from the EPA.
The EPA commented that the commission should provide further explanation
in the 42 USC, §7545(c)(4)(C) waiver request for what other control measures
were examined and the reasons for discarding these measures.
The commission believes that sufficient data are being provided in Appendix
L of the HGA Post-1999 ROP/Attainment Demonstration SIP regarding the various
alternate control strategies that were reviewed to determine whether the proposed
implementation of the LED fuel control strategy is justified to be included
as part of the attainment demonstration. The commission revised Appendix L
to ensure that the waiver request addresses the EPA concerns.
The EPA commented that the commission should better address in the 42 USC, §7545(c)(4)(C)
waiver request the reasoning for expanding the on-road measure of the proposed
rules statewide and why it is necessary for attainment. UDS expressed opposition
to the state-wide coverage of the proposed rules and asked why the commission
is requiring all of the citizens of Texas to share the cost burden associated
with the proposed rules when their additional costs provides so little real
benefit to the HGA area. UDS further added that this strategy should not be
extended to other areas that are currently in attainment, or who may be designated
nonattainment this summer, and that the commission should examine all potential
cost effective strategies before implementing a regulation mandating a fuel
standard as stringent as the proposed LED standard. ExxonMobil commented that
the commission has not shown a scientific basis for requiring state-wide coverage
for the proposed rules, nor has it demonstrated that state-wide boutique fuels
are necessary to attain the ozone standard in the HGA area. ExxonMobil further
added that the commission has shown no demonstration that the proposed fuel
is necessary to maintain air quality in attainment areas. Koch commented that
state-wide application of a rule designed to bring a nonattainment area into
attainment is inappropriate from outright lack of air quality need. BCCA commented
that a boutique fuel is not needed to maintain attainment outside of the HGA
area and that requiring a special, boutique fuel for areas of Texas that are
in attainment with all air quality standards has no technical, regulatory,
or legal basis.
As noted in the rule preamble, the commission expanded the rules to cover
the entire state as a means to help alleviate concerns regarding out-of-area
refueling practices in relation to the nonattainment counties and to reduce
the regional transport of ozone precursors. Federal and state studies have
shown that pollution from one area can affect ozone levels in another area.
This work is supported by the findings of the OTAG study, which is the most
comprehensive attempt ever undertaken to understand and quantify the transport
of ozone. Both the commission and the OTAG study results point to the need
to take a regional approach to control air pollutants, such as that prescribed
in the rules. The state-wide implementation of LED fuel will help reduce the
amount of NO
x
being transported into the HGA,
BPA, and DFW ozone nonattainment areas and other areas of the state having
concerns over air quality. The state-wide coverage will also provide a greater
market for diesel fuel producers and importers to provide the fuel required
by these regulations. The commission and local area evaluated over 250 possible
strategies while developing the attainment demonstration. These were identified
in Appendix L of the SIP submittal. Modeling assessing the benefits of these
rules demonstrated that by the year 2007, the use of LED will reduce NO
Koch commented that the commission should consider allowing marketable
credit for the use of premium diesel fuels, which use advanced performance
additives to achieve superior deposit control and corresponding in-use emission
benefits, instead of mandating a low emission diesel fuel. AAE commented that
its OxyDiesel clean diesel fuel formulation should be included in the proposed
rules among the options for the HGA area for on-road and nonroad diesel-powered
vehicles and equipment.
The rules allow the use of alternative formulations that provide emission
reductions equivalent to the specified fuel content standards for aromatics
and cetane. However, the alternative formulation must comply with the sulfur
standard as specified in the rule. The commission made no change to the rule
language in response to this comment.
Corpus Christi expressed opposition to the commission proposal to include
Nueces and San Patricio Counties in the coverage area of the proposed rules
and requested comment on how the boundaries of the coverage area were determined
and justified. Corpus Christi further requested comment on how the commission's
accelerated implementation schedule, as compared to the proposed federal implementation
schedule, can be justified in Nueces and San Patricio Counties. These counties
are remote from the HGA area, are currently in attainment of the ozone NAAQS,
and any benefit to the air quality of the HGA area from the fuel purchased
in Corpus Christi would be non-detectable. PCCA and Port Industries commented
that unless sound science demonstrates that emissions from the Corpus Christi
area, an attainment area, contribute to the nonattainment status of the HGA
or other nonattainment areas, the commission should refrain from imposing
controls on Nueces and San Patricio Counties and recommended that Nueces and
San Patricio Counties be removed from the proposed coverage area. Port Industries
further added that the commission should support a renewal of the Flexible
Attainment Region agreement that has proven successful in the Corpus Christi
area and that the commission should support initiatives for voluntary efforts
instead of the proposed mandatory requirements.
These rules are an element of an integrated regional ozone control strategy.
The commission has expanded the rules to cover the entire state as a means
to help alleviate concerns regarding out-of-area refueling practices in relation
to the nonattainment counties and to reduce the regional transport of ozone
precursors. Federal and state studies have shown that pollution from one area
can affect ozone levels in another area. This work is supported by the findings
of the OTAG study, which is the most comprehensive attempt ever undertaken
to understand and quantify the transport of ozone. Both the commission and
the OTAG study results point to the need to take a regional approach to control
air pollutants, such as that prescribed in the rules. The state-wide implementation
of LED fuel will help reduce the amount of NO
x
being transported into the HGA, BPA, and DFW ozone nonattainment areas and
other areas of the state having concerns over air quality. As such, the commission
is not removing the Corpus Christi area from the clean diesel regulations.
The state-wide coverage will also provide a greater market for diesel fuel
producers and importers to provide the fuel required by these regulations.
The commission revised the rule to delete the proposed requirements which
would have required 30 ppm sulfur by May 1, 2004 in order to be consistent
with anticipated federal rulemaking and implementation schedules.
Montgomery County commented that the elimination of Montgomery County from
the proposed rule coverage area would result in a difference of 1/200th of
a ppb (0.005 ppb) of ozone and recommended that Montgomery County be exempted
from the proposed rules. The Liberty County Sheriff commented that the commission
should exempt Liberty County from the proposed rules.
The FCAA Amendments of 1990 provided new requirements for areas that had
not attained the NAAQS for ozone, carbon monoxide, particulate matter, sulfur
dioxide, nitrogen dioxide, and lead, and new requirements for SIPs in general.
The EPA was authorized to designate areas failing to meet the NAAQS for ozone
as nonattainment and to classify them according to severity. FCAA, §107(d)(4)(A)(iv)
mandated that areas designated as serious, severe or extreme for ozone that
were within a metropolitan statistical area (MSA) or CMSA must have boundaries
that include the entire MSA or CMSA. This requirement is supported by the
legislative history for the FCAA Amendments in Senate Report No. 101-228,
page 3399, "Because ozone is not a local phenomenon but is formed and transported
over hundreds of miles and several days, localized control strategies will
not be effective in reducing ozone levels. The bill, thus, expands the size
of areas that are defined as ozone nonattainment areas to assure that controls
are implemented in an area wide enough to address the problem." The FCAA Amendments
did provide the ability to exclude portions of the entire MSA or CMSA prior
to designation, if the state conducted a study that EPA agreed proved that
the geographic portion did not contribute significantly to violation of the
NAAQS.
Montgomery County is a nonattainment county. Redesignation has not occurred
for any portion of the HGA nonattainment area, and is not currently being
considered. For existing areas currently included within a nonattainment area,
the specific area must be redesignated as attainment to be removed from a
nonattainment area. FCAA, §107(d)(3) provides that EPA may not redesignate
a nonattainment area, or a portion thereof, to attainment unless several criteria
are met, which include: a determination that the area has attained the NAAQS;
there is a fully approved SIP for the area; there is a determination that
the improvement in air quality is due to permanent and enforceable reductions
in emissions; there is an approved maintenance plan for the area; and the
state has met all requirements for the area under FCAA, §110 and Part
D.
However, even if a specific area within the HGA nonattainment area was
redesignated by the EPA as attainment for ozone, reductions associated from
all adopted ozone control strategies would still be necessary because of the
requirements of FCAA, §107(d)(3) and §175A which require maintenance
plans for all redesignated areas. The maintenance plan must include the measures
specified in §107(d)(3) and any additional measures that are necessary
to ensure that the area continues to be in attainment with the NAAQS for ten
years after the redesignation. Eight years after the redesignation, the state
is required to submit an additional revision to the SIP for maintaining the
NAAQS for ten years after the end of the first ten-year period.
Additionally, reductions associated from the ozone control strategies that
will be implemented outside the HGA nonattainment area will benefit the HGA
nonattainment area. This is due to the regional nature of air pollution, the
contribution from mobile sources, and the economies of scale and associated
market advantages related to distribution networks for some strategies.
At the time the 1990 FCAA Amendments were enacted, the focus on controlling
ozone pollution was centered on local controls. However, for many years an
ever increasing number of air quality professionals have concluded that ozone
is a regional problem requiring regional strategies in addition to local control
programs. As nonattainment areas across the United States prepared attainment
demonstration SIPs in response to the 1990 FCAA Amendments, several areas
found that modeling attainment was made much more difficult, if not impossible,
due to high ozone and ozone precursor levels entering from the boundaries
of their respective modeling domains, commonly called transport. Recent science
indicates that regional approaches may provide improved control of ozone air
pollution.
The commission conducted air quality modeling and upper air monitoring
that found regional air pollution should be considered when studying air quality
in Texas' ozone nonattainment areas. This work is supported by research conducted
by the OTAG, the most comprehensive attempt ever undertaken to understand
and quanitfy the transport of ozone. Both the commission and the OTAG study
point to the need to take a regional approach to controlling air pollutants.
The AAR, ASLRRA, and Union Pacific commented that there is no data showing
that diesel fuel meeting the proposed fuel parameters would have a beneficial
effect when used in locomotives, especially considering the significant increase
in costs that would occur. The AAR, ASLRRA, and Union Pacific further added
that while EPA is considering adoption of stringent sulfur limitations for
the purpose of enabling new engine and after-treatment technologies that are
sensitive to sulfur, it has not suggested that railroads would be subject
to these new requirements since locomotive manufacturers are not expected
to rely on the technologies the EPA has identified as being sensitive to sulfur,
such as catalysts and particulate filters, for the foreseeable future.
The commission believes that the reduced sulfur and aromatic content level
and the increased cetane level in the LED fuel will provide an emissions benefit
when used in locomotive engines and that the control of non-road diesel fuel
is necessary in terms of retrofit technology for demonstrating attainment
with the ozone NAAQS. The use of LED fuel will be beneficial to areas of the
state that are currently seeking voluntary actions from the railroad industry
to use newer technology engines while operating in their areas. There are
additional reductions of emissions when the low sulfur level is coupled with
a reformulation that has lower diesel fuel aromatic content regardless of
engine technology. The commission made no change to the rule language in response
to this comment.
Two individuals commented that mandates for cleaner buses and big trucks
are also necessary. Two individuals commented that the commission should require
all city buses, big trucks, and other transportation to use 'clean fuel,'
by 2007.
There are many federal and state mandates for reducing emissions from transit
buses and large trucks, including the EPA Urban Bus Rebuild Program, the EPA
2004 heavy-duty engine standards, the EPA expanded Tier II engine standards
(up to 14,000 pounds (lbs) GVWR), and the Texas Clean Fleet Program (up to
26,000 lbs GVWR). The EPA is also proposing new 2007 heavy-duty diesel engine
standards. Regarding clean fuel, the state rules will require ultra-low sulfur
LED for on-road and non-road use in the DFW and HGA nonattainment areas and
an additional 95 central and eastern Texas counties by 2007. The commission
made no change to the rule language in response to this comment.
Paso del Norte commented that the commission should be moving toward the
use of cleaner alternative fuels rather than requiring cleaner diesel fuel.
One individual commented that the commission should provide incentives for
the use of compressed natural gas (CNG), liquified natural gas, ultra-low
emission vehicles, and catalysts and filters on all internal combustion engines
and that the state road tax should be used to fund the incentives. One individual
commented that the commission should promote the use of propane as a transportation
fuel. One individual commented that the commission should promote the use
of CNG. Air Surrey commented that it had a software tool the commission could
use to justify and speed up the switch over from gasoline and diesel to relatively
non-polluting compressed natural gas motor vehicle fuel in the state's urban
areas. One individual commented that alternative fuels have not been fully
proven.
The commission acknowledges that the use of alternative fuels in specific
situations may provide air quality benefits and that tax credits are one of
many incentive strategies that could be used to promote the use of alternative
fuels. The commission chose to regulate diesel because the greater penetration
of the fuel in heavy-duty market will result in faster reductions of NO
TWOA commented that the proposed rule would be ineffective in regard to
tug/towboat applications due to the fact that 15 ppm sulfur diesel would be
more expensive, causing tug/towboat operators to avoid fueling in the HGA
area. WTC commented that the commission cannot enforce the proposed rules
on tug/towboat operations as the majority of its fuel is purchased outside
of the state and the commission's jurisdiction.
The commission acknowledges that there could be an estimated $.08 per gallon
increase in fuel costs as a result of these rules. The commission also acknowledges
that it has no jurisdiction outside the borders of this state. These rules
are enforced against the diesel fuel suppliers, not the users. The commission
recognizes that some out-of-state refueling may occur and has therefore broadened
the program area to lower the likelihood that will occur.
TWOA commented that requiring tug/towboats operating in the HGA to utilize
15 ppm sulfur diesel fuel creates safety risks because many tug/towboat engines
utilize diesel fuel as a lubricant and the drier ultra-low sulfur diesel could
cause failures of these engines thereby creating collision and pollution hazards.
The commission disagrees with this comment. All currently used or proposed
low sulfur diesel fuels are designed to meet the ASTM viscosity specification
or the ASTM standard for lubricity. The low sulfur diesel fuels currently
in use, such as CARB diesel (15 ppm), Swedish diesel (10 ppm), ARCO-BPAmoco
(9 ppm), have not demonstrated any lubricity problems with the fuel injection
and/or supply systems. Since the low sulfur diesel fuels are designed to meet
the specification for lubricity based on ASTM standards, there should be no
lubricity problem associated with fuel systems due to their ultra-low sulfur
contents. The commission made no changes to the rule language in response
to this comment.
TWOA requested comment on how does the commission propose to overcome the
mixing of multiple fuels with multiple sulfur contents, from multiple tug/towboats
coming from multiple states and how is the commission going to assure the
EPA that the proposed rule will actually reduce the sulfur level of fuels
to 15 ppm. TWOA further requested comment on how has the commission accounted
for the sulfur contents of oils that enter the engine and increase the sulfur
content of the fuel beyond 15 ppm. Three individuals commented that the commission
should consider measures to ensure trucks crossing borders into Texas, or
from other Texas regions, are also running on low sulfur diesel. One individual
commented that the commission needed to implement a widely deployed field-test
system to rapidly determine if a vehicle's fuel is contaminated with high-sulfur
fuel.
The commission acknowledges that it cannot control out-of-state or country
fuel purchases and that there may be commingling of fuel with differing sulfur
levels in individual vessels and vehicles. The rules apply to the distribution
of LED within the covered area, not whether individual vehicles may have noncompliant
fuel within their fuel tanks. However, the rules will ensure that local fuel
purchases comply with the LED sulfur requirements. In addition, the proposed
EPA 2007 heavy-duty diesel engine and vehicle standards and highway diesel
fuel sulfur control requirements which require the nationwide use of 15 ppm
sulfur for on-road motor vehicles in June 2006 will help alleviate concerns
over commingling.
While diesel engine lubricating oils do indeed have a relatively high concentration
of sulfur (2,500 - 8,000 ppm by weight), these oils do not appear to have
a large impact on exhaust sulfur levels. According to EPA's
Draft Heavy-Duty Standards Regulatory Impact Analysis
of May 2000,
the equivalent fuel sulfur level increase resulting from a 5,000 ppm lubricant
is approximately one ppm. Therefore even at fuel sulfur levels as low as 15
ppm, incremental increases remain quite low.
In addition, the sulfur standard is proposed primarily for the purposes
of technology enablement, allowing aftertreatment devices such as selective
catalytic reduction (SCR) to operate properly in the future. However, the
commission's emission benefit calculations do not account for the effect of
such devices by 2007. Since an increase in sulfur does not increase NO
TWOA strongly recommended that the commission remove the tug/towboat industry
from the proposed rule because of the insurmountable issues associated with
engine performance and the fact that the majority of the diesel fuel used
by this industry is purchased outside of the area under the jurisdiction of
the commission.
The control strategies being implemented by the commission in the HGA nonattainment
area are necessary to the area's federal requirement to demonstrate attainment
by 2007 and all possible reductions are needed. The commission believes that
tug/tow boats are a contributing emission source in the HGA area and that
it would not be appropriate to exclude them from these rules. The commission
made no change to the rule language in response to this comment.
Sierra-Galveston commented that the commission should adopt the California
standards for low sulfur fuels.
The commission believes that the LED fuel program will provide more emission
reductions benefits than California diesel fuel standards, mainly due to the
addition of minimum cetane requirements in the Texas rules. The commission
made no change to the rule language in response to this comment.
GEHC commented that the commission could solve a lot of the pollution reduction
problems with airport ground equipment, large trucks, locomotives, and marine
vessels by requiring cleaner-burning diesel fuel.
As noted in the rule preamble, the rule requires LED for on-road use statewide
and for both on-road and non-road use in the DFW and HGA nonattainment areas
and an additional 95 central and eastern Texas counties in the regional area.
The requirement for non-road use of LED will impact airport ground equipment,
locomotives, and marine vessels equipped with diesel fueled engines and large
diesel fueled trucks will be impacted by the on-road LED use requirement.
The commission made no change to the rule language in response to this comment.
One individual commented that the commission should consider other options
that should include forcing refineries to change diesel formulations to remove
more toxins.
The commission shares the commenter's concern regarding toxins. The commission
anticipates that the limits on aromatics in the rules will result in reductions
in toxics in diesel fuel. The commission made no changes in the rule language
in response to these comments.
One individual commented that requiring the use of low sulfur/low aromatic
fuels for all types and forms of internal combustion (I/C) engine use has
been delayed too long and that Sweden and Germany are moving to ten ppm sulfur
liquid fuels and expect to market five ppm fuel.
The commission is aware of the diesel fuel standards that are being proposed
for Europe. However, the NO
x
benefits of ultra-low
sulfur diesel fuels are dependent upon advanced emission control technologies,
such as NO
x
catalytic converters and particulate
filters. Requiring such fuels before the technology is available does not
guarantee NO
x
emission reductions. The commission's
timing of the sulfur requirement is to ensure that it is available when federal
diesel engine standards are implemented.
One individual commented that the cost of plant modification distributed
over 20 years of plant life must be considered against the reduced costs of
child and adult health care accruing from breathing cleaner air with reduced
ozone and PM concentrations.
The commission evaluated previous studies, such as those conducted by the
EPA and the DOE, regarding the estimated economics of producing low sulfur
diesel fuel and believes that these studies provide sufficient cost benefit
analysis to justify the data included in the fiscal impact section of the
rule preamble. The commission agrees with the commenter that the benefits
of these rules include public health improvements.
Three individuals commented that low sulfur/low aromatic gasoline and diesel
fuels are essential for the effective use of current catalytic and filter
technologies to reduce I/C engine exhaust-gas pollutants and be consistent
with an acceptable catalyst life, avoiding catalyst poisoning.
The commission agrees with this comment.
One individual commented that a tax relief credit for conversion to, and
use of, low sulfur fuels should be made available for three years. Alternatively
the excise tax on this fuel must make it cheaper per gallon at the pump than
non-reformulated equivalent fuel. A well-funded Carl Moyer type program would
help the multiple small firms make the conversion. One individual commented
that the commission should promote the use of low sulfur, low aromatic fuels
and subsidize the cost so that these fuels are less expensive than the standard
fuels.
The commission agrees that economic incentive programs can potentially
be an effective tool for achieving air quality. One such program is the Carl
Moyer program in California. That program appears to be successful in providing
flexibility to the regulated industry while still achieving reductions in
air emissions. The California program is authorized by and funded through
the state legislative process and such legislative approval does not currently
exist for a similar Texas program. The commission will continue to try to
identify economic incentives which it has authority to implement. Because
the commission agrees that market-based incentive programs can be an important
component in encouraging development of new technologies and/or greater or
more cost-effective emission reduction strategies, the commission provided
for the inclusion of economic incentive programs as a component of the HGA
SIP in the future.
The commission does not have the authority to make changes to any state
taxes or offer fuel tax credits. Only the legislature has the authority to
modify state tax regulations. Currently, 30 TAC Chapter 117, Tax Relief for
Property Used for Environmental Protection, is the commission's program that
provides tax relief for the purchase of pollution control property. On November
2, 1993, the voters of Texas approved a constitutional amendment, commonly
referred to as "Proposition 2," that provides an exemption from property taxation
for pollution control property. The intent of the constitutional amendment
was to ensure that capital investment undertaken to comply with federal, state,
or local environmental mandates did not result in an increase in a facility's
property taxes. Legislation implementing that amendment, House Bill 1920,
was passed during the 73rd Texas Legislative Session which added a new §11.31
and §26.045 to the Texas Tax Code (Tax Code). The Tax Code provides that
pollution control property could include any land purchased after January
1, 1994, or any structure, building, installation, excavation, machinery,
equipment, or device and any attachment or addition to or reconstruction,
replacement, or improvement of property that is used, constructed, acquired,
or installed wholly or partly to meet or exceed rules or regulations adopted
by any federal, state or local environmental agency for the prevention, monitoring,
control or reduction of air, water, or land pollution. Motor vehicles are
specifically noted as being ineligible for an exemption under this provision
of the Tax Code. The Tax Code contains a two-step process for securing an
exemption from property taxes for pollution control property. An applicant
must first receive a determination from the commission that the property is
used for pollution control purposes. The applicant then can use this determination
to apply to the local appraisal district for a property tax exemption. The
commission made no change to the rule language in response to this comment.
Koch and TxOGA expressed strong concerns that LED product availability
was not given proper consideration in the proposed rulemaking and the timing
is out of sync with the proposed federal diesel requirements. CITGO, ExxonMobil,
Koch, Lyondell-CITGO, NPRA, TxOGA, and Valero expressed concern that the proposed
rule will lead to supply disruptions and product outages as well as price
volatility which will have a severe negative impact on supplies of on-road
and non-road diesel fuel in the state. BCCA commented that the proposed LED
presents a much higher market risk and uncertainty for diesel supplies throughout
east Texas than the proposed federal low sulfur diesel fuel rule because the
proposed LED rule will reduce regional diesel fuel supplies, reduce incentives
for refiners to invest in low sulfur diesel facilities, and limit refiner's
ability to build new facilities. TCSE commented that requiring the sale of
more costly low emission diesel will cause tremendous economic disruption
in the state and hurt the public.
The commission revised the rule to delete the proposed requirements which
would have required 30 ppm sulfur by May 1, 2004 in order to provide greater
flexibility for producers to comply with these rules and to be consistent
with anticipated federal rulemaking and implementation schedules.
TxOGA commented that even if the refiners willing to comply with the proposed
LED requirements can manufacture sufficient supplies of LED, it does not believe
that the existing distribution system can provide continuous and ample supplies
of a 15 ppm diesel fuel for Texas while products containing significantly
higher sulfur levels are being shipped in the same delivery system. BCCA commented
that the existing fuels distribution infrastructure is not currently sufficient
to deliver Texas boutique fuels to the marketplace in a timely fashion. NATSO
and NPRA expressed opposition to the proposed reduction in sulfur to 30 ppm
in 2004, a full two years ahead of the proposed federal standard, and commented
that it would seriously jeopardize the integrity of the region's fuel supply
and delivery system and place both supply and demand for the ultra-low sulfur
fuel at risk, thereby seriously jeopardizing the success and viability of
the proposal. NATSO further added that the proposed rule requiring 30 ppm
sulfur levels in 2004 could seriously disrupt the travel plaza and truck stop
industry's ability to consistently and reliably acquire highway diesel fuel
for retail sales and would place those diesel retailers in the covered areas
under the 2004 proposal at a significant competitive disadvantage when compared
to those diesel retailers in other area of Texas and neighboring states not
covered by the proposal by requiring them to sell a fuel that would be almost
impossible to acquire. NATSO commented that the proposed 30 ppm sulfur diesel
required in 2004 would need to be segregated from the 500 ppm fuel throughout
the state's distribution chain to prevent cross contamination and the added
costs to segregate these fuels would further drive up fuel prices. Valero
commented that the logistics of distributing "boutique" fuels ahead of the
federal regulations to the eastern half of Texas is a practical impossibility.
CITGO commented that refiners that supply both the Texas market and the Colonial/Explorer
pipeline systems will have to have separate tanks to store the ultra-low diesel
required in the Texas market in 2004 from the federal diesel being supply
to the rest of the nation and that the tankage does not exist today to support
an additional grade of diesel fuel that will only serve the Texas market.
CITGO further added that the current tankage and logistics systems in refiners
were not designed to protect product qualities down to the significantly ultra-low
sulfur levels being proposed, especially when higher sulfur products are being
handled in the same system. CITGO, Phillips 66, and TxOGA commented that a
study conducted by the National Petroleum Council,
U.S. Petroleum Refining: Assuring the Adequacy and Affordability of Cleaner
Fuels,
June 2000, concluded that there was a doubt on whether the distribution
system can handle ultra-low sulfur product and maintain the integrity of the
sulfur level as long as higher sulfur products are being shipped in the same
system. TMTA commented that the proposed rule will fragment the diesel fuel
supply by requiring multiple types of diesel fuel within the state: a Western,
an Eastern/Central, and a Houston/Galveston diesel, and this fragmentation
will strain the state's diesel production and distribution system, leading
to supply shortages and exorbitant prices. BCCA commented that the proposed
LED rule will create an additional grade of diesel to be blended and distributed
through systems that are already stretched beyond design and that there are
serious and real concerns that it will not be possible to blend and distribute
the boutique fuels throughout Texas while providing the rest of the country
with EPA-specified fuels.
The commission acknowledges that the distribution system may have difficulties
in segregating ultra-low sulfur diesel from other higher sulfur products.
However, the commission believes that these issues can be overcome, as was
shown by the industry's previous experiences with reformulated gasoline and
low sulfur highway diesel fuel. The commission is confident that the industry
will be able to provide compliant fuel in sufficient quantities to supply
the Texas market and do so in a timely fashion to prevent major supply disruptions.
The commission revised the rule to delete the proposed requirements which
would have required 30 ppm sulfur by May 1, 2004 in order to provide greater
flexibility for producers to comply with these rules and to be consistent
with anticipated federal rulemaking and implementation schedules.
NATSO also commented that the proposed rule requiring 30 ppm in 2004 would
essentially prohibit influx of foreign supplies of diesel fuel, which could
otherwise be used to ease shortages in domestic production and supply, since
the highway diesel fuel required in the covered areas would have a lower sulfur
level than highway diesel produced in most other countries.
The commission revised the rule to delete the proposed requirements which
would have required 30 ppm sulfur by May 1, 2004 in order to provide greater
flexibility for producers to comply with these rules and to be consistent
with anticipated federal rulemaking and implementation schedules.
Ato Fina and BCCA commented that the proposed implementation schedule does
not allow sufficient time for the refining industry design, engineer, permit,
procure equipment, construct, and begin production of the new fuel. ExxonMobil,
Koch, NPRA, and UDS commented that the implementation schedule is unrealistic
since refinery and infrastructure changes are not only costly but time consuming
and it is not realistic to stipulate that major fuel property changes occur
slightly more than a year after promulgation of regulations. Koch further
added that a minimum of four years lead time is necessary in the best of times
to plan, engineer, permit, construct, and test the additional diesel refining
units needed to comply with the proposed fuel standard and that the unprecedented
changes in gasoline properties that have been promulgated by the EPA as well
as other voluntary actions that have been adopted by various refiners has
extended engineering design and construction as never before and the time
schedule for any other requirements can be expected to be longer than usual
because of the enormous demand on finite resources. CITGO and NPRA commented
that implementing new diesel fuel sulfur standards in 2002, 2004, and 2006
will certainly exceed the capacity of the industry's engineering and construction
resources. CITGO, NPRA, and UDS commented that the proposed implementation
date of May 1, 2002 does not allow adequate lead time for refiners to build
the facilities needed to comply with the LED specifications and that the commission
should not implement a diesel fuel standard that will require engineering
and construction schedules for diesel desulfurization facilities to overlap
with those of refinery facilities that will be built to meet the federal Tier
II and other gasoline requirements. CITGO further added that overlapping the
schedules for the federal and state gasoline and diesel fuel projects will
increase the costs of both programs, as these projects will compete for the
same scarce resources and both projects will be competing for permit approvals
from state agencies, which are unlikely to have the resources to expedite
the approvals even if they wished to do so. NPRA commented that the 30 and
15 ppm sulfur caps proposal exacerbates the competition for scarce construction
and engineered equipment resources and that the commission should take these
concerns into account and develop a more rational schedule for fuel specification
changes. Valero recommended that the proposed rules be harmonized with the
federal rules to prevent supply disruptions in Texas. ExxonMobil recommended
that the commission use the maximum implementation schedule allowed by federal
law and EPA policy as an alternative to the 2004 schedule and allow the installation
of controls up until the HGA ozone attainment year of 2007 to alleviate much
of the projected labor, material, and equipement shortfall and reduce the
number of unscheduled shutdowns.
The commission acknowledges that the implementation schedule may be difficult
for some producers to comply with if major refinery modifications are required.
However, the 2002 implementation date does not require any further reductions
in sulfur than required by current federal regulations and the rules allow
the producer to use an approved alternative diesel fuel formulation if it
is equivalent in emission reduction benefits to fuel meeting the rules' aromatic
and cetane standards. The commission acknowledges that refinery modification
will be required to comply with the 2006 sulfur standards and made all permit
requests regarding facilities modifications or new construction to comply
with the LED rules or the EPA Tier II low sulfur gasoline regulations top
priority within the commission permitting process. The commission anticipates
these types of permits will be processed within nine months of receipt, if
uncontested. The commission believes that the industry is already planning
refinery changes to meet both the EPA Tier II low sulfur gasoline and the
proposed federal ultra-low sulfur diesel rules and should be able to complete
these projects within the frame work of the rules' implementation schedule.
TMTA requested that the commission provide the public with the substantive
materials that were used to develop the proposed rule and that the materials
used to determine the feasibility and cost of distributing, storing, and retailing
this stew of diesel fuels should also be provided to the public so that the
industry can determine how the commission expects the Texas distribution system
to respond when shortages or strong demand tax the fuel supply in different
parts of the state.
The commission believes that sufficient fiscal impact information was provided
in the fiscal note section of the rule proposal preamble. The commission believes
that the current diesel fuel distribution system is adequate to handle the
requirements of the rules and does not anticipate major supply shortages as
a result of these rules. The commission is confident that the petroleum industry
will be able to provide compliant fuel in sufficient quantities to supply
the Texas market and do so in a timely fashion to prevent major supply disruptions.
The commission has made no change to the rule language in response to these
comments.
MECA expressed support for the proposed rules and commented that the availability
of diesel fuel with very low sulfur levels is critical in maximizing the effectiveness
of exhaust PM control technologies on the widest range of engines and that
the proposed 30 ppm cap followed by the 15 ppm cap on diesel fuel for both
non-road and on-road engines will greatly facilitate the utilization and optimization
of the full range of control technologies for maximum control efficiency and
will insure reliable and durable operation.
The commission appreciates the support. However, the commission revised
the rule to delete the proposed requirements which would have required 30
ppm sulfur by May 1, 2004 in order to provide greater flexibility for producers
to comply with these rules and to be consistent with anticipated federal rulemaking
and implementation schedules.
Valero commented that it has no plans to upgrade its Texas refineries ahead
of the federal rules to produce "boutique" fuels and will be forced to participate
in the Texas market only as economics dictate. CITGO and ExxonMobil expressed
concern that Texas refiners who are unable or unwilling to make the significant
investments to address cetane and aromatics will find alternate deposition
for the diesel volume they currently supply to Texas and that product availability
will diminish significantly, creating fuel supply disruptions and dramatic
price increases. UDS commented that Texas refineries currently export a large
portion of their diesel outside of Texas and thus, have an alternative to
supplying a boutique fuel to Texas markets.
The commission acknowledges that some producers may make the decision not
to compete in the Texas market based on their inability or unwillingness to
comply with the requirements of the rules. However, the commission is confident
that the market will be supplied by existing producers that do make the investment
to supply the market and by producers that may not have entered the Texas
market in the past.
Koch and NATSO commented that the investment costs are underestimated and
that fuel prices are estimated to be at least two to three times more than
the commission's estimates. Metro commented that the estimated increase cost
of $.08 per gallon is too optimistic and it is more likely that the cost of
diesel fuel will increase in more severe increments and with higher frequency
than considered in the proposed rule. AAR, ASLRRA, and Union Pacific commented
that the commission significantly underestimated the effect this proposed
rule will have on fuel prices because the infrastructure to produce and distribute
diesel fuel meeting the proposed specifications is not in place in Texas,
there have been no analysis of whether the prices that railroads and other
ultimate purchasers of diesel fuel would pay for this special diesel and the
price comparisons commensurate with increased production costs, and the price
comparisons fail to consider actual differences in fuel prices or the recent
spikes in fuel prices. CITGO commented that their experiences with producing
maximum 15 ppm LED fuel has shown that the more frequent catalyst replacement
needed to maintain the 15 ppm sulfur cap raises the cost of production by
about $.07 per gallon, excluding capital recovery, and if CITGO is required
to decrease aromatics and/or raise the cetane levels, the investment and operation
costs will increase even more. TABCC commented that the proposed fuel is estimated
to cost consumers and businesses $.12 to $.14 more per gallon and will be
subject to price spikes like those observed in the Chicago area this past
summer. NPRA commented that the cost of the first phase of the proposal may
be understated since California diesel, which is similar to the proposed LED,
has maintained a retail price difference much higher than the $.04 per gallon
estimated by the commission. BCCA commented that the production cost of the
proposed LED fuel in 2002 to be in the same league as CARB diesel, or about
$.09 per gallon, based on the CARB diesel market place experience, since the
two fuel specifications are similar. BCCA further added that the production
cost to go from the 500 ppm sulfur level in the proposed LED in 2002 to the
15 ppm sulfur LED proposed for 2006 will be comparable to the cost to produce
the proposed federal ultra-low sulfur diesel (15 ppm sulfur), or about $.10
per gallon, and therefore, unless there is a desulfurization technology breakthrough,
or new refining process synergies developed, the combined cost for the proposed
LED program in 2006 is estimated to be over two times higher than the commission
estimate of $.08 per gallon. Five individuals commented that ultra clean fuels
will carry high prices. PCCA commented that from the standpoint of cost to
produce, benefits derived versus the increased costs to make the fuel makes
the proposed requirements cost-prohibitive and worthy of reconsideration by
the commission. ExxonMobil commented that the commission not provided valid
and adequate cost estimates and economic impact analyses for the proposed
2004 implementation schedule.
According to a CARB publication entitled,
California
Diesel Fuel Factsheet,
published in March 1997, a gallon of California
diesel fuel costs approximately $.01 to $.04 more to produce than diesel fuel
in other states. While other factors beside production costs can and do affect
the retail prices of diesel fuel in California, the commission contends that
production costs are the most stable measure for comparison analysis. A recent
report published by the California Attorney General's Office entitled,
A comparison of the weekly average retail prices for on-highway diesel
fuel published by the DOE for the week ending October 16, 2000 showed retail
prices of California diesel to be $.16 more expensive than the retail prices
of diesel fuel sold in the Gulf Coast region and $.10 more expensive than
the national average. However, the commission contends that the $.04 increase
in production costs is a valid determination of the costs associated with
the proposed rules since other factors which could affect retail prices, as
indicated above, are not the same in Texas as those in California.
The commission agrees with the comments that the actual retail price could
be more expensive than just the difference in production costs. However, the
commission is not aware of any firm method of determining what the actual
retail price of LED fuel will be in May 2002 or in June 2006 and what factors
will be affecting the price difference to that of conventional diesel fuel.
In addition, the commission believes that new refining technologies for reducing
sulfur, such as the recently introduced Phillips 66 "S Zorb" technology and
BP's OATS process, could significantly reduce production costs and could help
alleviate concerns over supply availability. The commission revised the rule
to delete the proposed requirements which would have required 30 ppm sulfur
by May 1, 2004 in order to provide greater flexibility for producers to comply
with these rules and to be consistent with anticipated federal rulemaking
and implementation schedules.
BCCA commented that based on learning from the CARB diesel experience and
recent estimates made by the EPA and Charles Rivers Associates for very low
sulfur diesel, it is estimated that the capital cost for statewide 2002 LED
will be $500 million.
The commission acknowledges that significant capital costs could be incurred
by some producers to meet the requirements of the rules and that the $500
million state-wide capital costs estimated by the commenter is comparable
to the calculations estimated by the EPA. According to the EPA analysis found
in the
Notice of Proposed Rulemaking on the Heavy-Duty
Engine and Vehicle Standards and Highway Diesel Fuel Sulfur Control Requirements,
the estimated capital costs for a typical refinery will be approximately
$31 million.
TDA commented that the commission should consider the financial impact
of the proposed rule on agriculture producers and that TDA would not like
to see more government regulations placed on this industry if they are not
necessary. BCCA commented that the commission has not considered the cost
of the proposed rule on operators of non-road diesel equipment.
As noted in the rule proposal preamble, the fiscal analysis only considered
on-road diesel vehicles because vehicle counts for non-road diesel vehicles
were not available. However, the commission believes that costs will be similar
for both on-road and non-road diesel vehicle users. The commission made no
change to the rule language in response to these comments.
UDS commented that many formulations covering the production of California
specification diesel are either patented or proprietary and therefore the
cost to produce this fuel by non-California refiners may be even higher than
in California itself.
The commission acknowledges that there may be issues with some producers
over patent infringement. However, the rules allow the use of California-certified
diesel fuel formulations as an option for compliance flexibility, not as a
requirement. The rules do not prohibit diesel fuel producers from submitting
their own diesel fuel formulations to California for certification and possibly
preventing any patent infringement issues. The commission is unable to adequately
address the issue of cost in this comment because the commenter did not provide
any estimates toward the possible cost of patent infringement issues. The
commission made no change to the rule language in response to this comment.
The Houston MPO commented that the commission should re-examine the NO
The commission is aware that CARB claims a higher potential emission reduction
(about 12%) for electronically-controlled diesel engines, using an equivalent
fuel specification. However, this estimate is based on limited testing of
a single engine from the early 1990's, using a simple fuel test matrix. The
commission's estimate of NO
x
benefits for the
proposed rules is based on extensive testing under the EPA Heavy-Duty Engine
Work Group (HDEWG), utilizing a sophisticated fuel matrix and a late-technology
engine using exhaust gas recirculation, representative of engines meeting
the upcoming 2004 standards. In addition, the 5.7% benefit estimate is more
in line with other recent findings for similar fuels, including a 4.1% value
obtained for 1998-equivalent engines under the European Auto-Oil study in
1999. Therefore, the commission believes the 5.7% value to be reasonable,
and representative of those late model, electronically-controlled engines
having the greatest emissions impacts in 2007. The commission made no changes
to the rule language in response to this comment.
NPRA commented that the commission's estimate of 30 tpd of NO
x
reduction in 2007 is too high and is a overstatement of the benefits
in Texas that can be realized by changing diesel fuel formulation and that
changing diesel fuel specifications without adding yet-to-be-commercialized
retrofit pollution control to existing vehicles results in limited NO
The commission disagrees with this comment. The EPA proposed 2007 heavy-duty
diesel engines standards will require engine manufacturers to utilize advanced
emission control systems to achieve the standards and these systems will require
the use of an ultra-low sulfur diesel fuel to be effective. The modeling associated
with these rules used the estimated emission reductions from 2004 model heavy-duty
engines using low sulfur diesel to estimate the claimed emission reductions
for existing diesel engines. The commission made no change to the rule language
in response to this comment.
UDS commented that emission benefits from boutique fuels may be overstated
since some diesel vehicles that are not centrally fueled and have sufficient
fuel capacity range will choose to purchase diesel outside of Texas, not only
in Louisiana, New Mexico, and Oklahoma, but also Mexico, especially if the
price differential between the EPA diesel and the proposed Texas LED is substantial.
TMTA requested the commission to expand its analysis to more thoroughly address
how freight contracts will shift to out-of-state companies offering cheaper
rates using cheaper non-compliant diesel fuel and how this will reduce the
rule's effectiveness. TMTA commented that given the proximity of the state's
nonattainment areas to adjacent state borders, any state diesel fuel requirement
can and will be avoided due to the higher cost of compliant fuel and that
this will lead to a proliferation of out-of-state trucking companies serving
the state.
The commission acknowledges that the possibility of out-of-state refueling
by diesel truck traffic does exist. The commission is not aware of any estimates
of the fraction of vehicle miles traveled (VMT) attributable to such "pass
through" truck traffic. Therefore, without additional information, the commission
is not able to estimate a reasonable offset factor for this effect. However,
the rules apply to all diesel sales for on-road use statewide and the commission
does not anticipate the impact of out-of-state refueling will be significant.
Nevertheless, the intent of the rules is to impact as large a fraction of
area-wide diesel VMT as is reasonable, which the commission believes will
be accomplished through these rules. The commission made no change to the
rule language in response to these comments.
BCCA, Koch, and TxOGA commented that the emission benefits of the proposal
are overestimated because the two prediction models, the HDEWG model for post
1990 engines and the CARB model for earlier engines, used by ERG to predict
emission benefits are extremely limited in scope and focus exclusively on
advanced technology engines meeting the 2004 and later emission standards.
Koch and TxOGA further added that the HDEWG study utilized large amounts of
cetane improver in the diesel used to conduct the study and that most diesel
fuel used in the HGA area does not contain cetane enhancers. Koch and TxOGA
commented that the commission should consider the conclusions drawn in the
Society of Automotive Engineers (SAE) Paper 982649,
Fuel Quality Impact on Heavy Duty Diesel Emission: A Literature Review,
in determining the benefits associated with the proposal.
The commission believes that while the uncertainty of the estimates from
mechanically-controlled diesel engines provided by the ERG study, which was
based on a small CARB data set operating on California diesel, is greater
than the uncertainty of the estimates for newer, electronically-controlled
engines, the claimed reductions are indeed reasonable and conservative. The
7.0% NO
x
emission reduction value is only slightly
higher than the 5.7% figure used for electronically-controlled engines in
this analysis. Also, the mechanically-controlled engines make up less than
2.0% of the on-road VMT by 2007, based on local registration distributions
and MOBILE5 default mileage accumulation rates. Therefore, for the on-road
sector the impact of any uncertainty in these figures is diminished by the
small size of the fleet under consideration.
In Phase I of the HDEWG testing, five to six fuel blends were sent to several
different engine manufacturers, including Cummins and Detroit Diesel, for
baseline testing. The EPA determined that the Caterpillar 3176 engine had
emissions typical of equivalent technology engines from other manufacturers.
These engines were selected to be representative of upcoming engines meeting
1998/2004 standards, according to the Southwest Research Institute (SwRI)
program manager. Therefore, the Caterpillar 3176 engine was deemed an appropriate
selection for further testing. This was the consensus among participating
manufacturer representatives as well.
While it is true that the fuel set used in the HDEWG test program is atypical,
the study could not have achieved its objective of determining parameter-specific
effects without some sort of manipulations of the blends involved. In addition,
SwRI technical staff involved in the test program point out that, by and large,
the fuel set parameters were selected to mimic the fuel properties anticipated
from advanced diesel fuel production in the near future. Finally, in regard
to cetane enhancers, the test program clearly demonstrated that there was
no significant difference in the interaction between natural or boosted cetane
levels and other effects such as aromatics-induced reductions. Therefore,
the pervasive presence of boosted cetane in the fuel matrix did not bias the
outcome of the test program.
The SAE Paper 982649, which summarizes the available research up to that
point on diesel fuel property impacts on emissions, cites a less than 5.0%
impact for total aromatic reductions from 30% - 10% by weight. However, the
authors of the paper themselves acknowledge that "on a percent basis, polyaromatics
should contribute more to NO
x
than a corresponding
amount of mono-aromatics." Thus, if polyaromatics are reduced disproportionately
compared to mono-aromatics, the reductions could be even greater than stated
above. Since the HDEWG predictive model accounts for both poly- and mono-aromatic
levels, the commission believes that the modeled result of 5.7% is within
the range of reasonable reductions. In addition, the SAE authors themselves
reference the ongoing work by the HDEWG as a source of future data concerning
the differential effect of aromatic species. The commission made no change
to the rule language in response to these comments.
Koch and TxOGA commented that the 2.5% emission reduction benefit claimed
by the ERG study, and used by the commission to estimate the NO
x
benefit of the proposed LED program, should be reduced to a 1.75%
NO
x
reduction benefit because the modeling in
the ERG study assumed a typical alternative diesel formulation at 20% aromatics,
compared to 10% aromatics required by the California diesel fuel standards.
Information provided in the SAE Paper 982649 showed 2.5% to be a reasonable
estimate only if aromatics were reduced from 30% - 10%.
The commission disagrees with this comment because all CARB certified alternative
diesel formulations must demonstrate equivalent emissions performance to the
base standard at 10% aromatics, and other parameters, such as cetane number,
are usually raised to compensate for an increase in aromatics. Accordingly,
the commission accounted for the modified parameters specified in the certified
alternative diesel formulations, including relative contributions of poly-
and mono-aromatics, in its modeling. Therefore, the fact that California diesel
fuels were modeled by the commission at 20% aromatics levels to emulate the
diesel fuel currently being used in California does not warrant the proposed
correction factor. The 0% - 5.0% range cited in the SAE Paper 982649 may also
be somewhat biased by the model year of the engines tested. Specifically,
of approximately ten engines used to generate the 0% - 5.0% estimate, all
but two were 1995 or older models (as old as 1991). Although more detailed
research would be needed to quantify the effect, the commission believes that
these engines most likely featured a higher pre-mix burn fraction than is
found in the most advanced engines today, such as the Caterpillar 3176 engine
tested by the HDEWG. This factor would tend to decrease the impact of aromatic
reductions somewhat for the relatively older engines. The commission made
no change to the rule language in response to this comment.
BCCA recommended that the commission remove the aromatic and cetane specifications
associated with the proposed rule since these specifications are much less
relevant when the new federal ultra-low sulfur diesel enters the market in
2006 followed by the low emission heavy-duty diesel engines in 2007. Ethyl
commented that raising the minimum cetane number of diesel fuel in Texas to
50 would meet or exceed the emission reduction targets presented in the proposal
and that no other fuel property changes, such as limiting aromatic hydrocarbons,
are needed. Ethyl further added that this strategy is an inexpensive NO
The federal low-sulfur diesel proposal only generates significant NO
The commission agrees that increasing cetane number appears to have a beneficial
impact on NO
x
emissions for current engine technologies.
However, the HDEWG study is the best (and only) study to date evaluating fuel
changes in 2004-compliant engines. This study found that cetane has a negligible
effect on these engines. Considering the "pull-ahead" of the 2004 standards
to the 2002 model year, and the disproportionately large contribution to total
VMT from heavy-duty trucks six years of age and newer, 2004-compliant engines
will have a very significant impact on on-road NO
x
emissions in 2007. Therefore fuel specifications must affect this portion
of the fleet as well as those engines meeting earlier standards. In order
to achieve the required reductions, fuel strategies will most likely have
to address both aromatics and cetane. While the commission is eager to evaluate
additional studies involving 2004-compliant engines when they become available,
judgements regarding fuel effects must be made given currently available information.
The commission agrees that manipulation of cetane number is likely to be
less expensive than aromatics changes. However, the commission does not agree
that cetane changes are the "only realistic solution" to the goal of NO
TxOGA commented that the proposed 10% aromatics limit may adversely affect
the seals used within diesel engines resulting in possible seal failures and
increased costs to the diesel engine user from otherwise unnecessary downtime
and the substantial labor and materials involved in engine repairs. One individual
commented that the commission should not implement the proposed rule if it
will cause damage to diesel engines. One individual commented that the commission
should make sure to adequately test new fuel formulas before imposing them
on Houston to ensure against seal failures.
Investigation by the EPA and the CARB has shown that the reduced aromatic
contents of low aromatic diesel fuels has contributed to fuel leaks in older
diesel engines and vehicles, mainly from the shrinkage and possible cracking
of the elastomeric seals, commonly known as O-rings, in some older diesel
engines, but not in every case. The change from a higher to a lower aromatic
fuel may cause elastomeric seals found in some older engines to shrink and
possibly crack, especially those seals made of nitrile rubber that have seen
long service at high temperatures. Commonly, the seals that failed were worn
considerably and due for replacement. Thus, the cost for the worn seal or
O-ring replacement would have to be incurred by the vehicle operator at some
point, regardless of the change in fuel. The commission suggests that proper
seal replacement and maintenance schedules will help prevent untimely equipment
failures. Studies have shown that after the replacement of these seals, the
occurrence of leaks was virtually eliminated.
In addition, the rules do allow alternative formulations of diesel fuel
to be used, including diesel fuel with a higher aromatic content than specified
in the rules, as long as the emission reduction performance of the alternative
formulation is equivalent to the specified LED fuel. The commission made no
change to the rule language in response to this comment.
Koch commented that the State of Texas seek any and all extensions to the
attainment deadline that might be available under law to allow enough time
for the federal fuel programs to deliver the emission reductions that are
so critically needed by the HGA area. Koch further added that Texas should
not be "forced" to adopt short-term stopgap measures that add enormous cost,
and essentially inconsequential benefits.
The FCAA requires that a state have no more than one exceedance of the
NAAQS in the year preceding the extension year, and that the state has complied
with all requirements and commitments in the applicable implementation plan,
prior to EPA granting such an extension. There is no provision in the FCAA
or EPA guidance for EPA granting an extension in the absence of this data.
However, the commission is committed to working with EPA and all interested
parties to provide opportunities for new, low-emission equipment availability
within the HGA nonattainment area.
The EPA commented that 42 USC, §7545(c)(4) preemption does not apply
to fuel content for non-road diesel engines and therefore no waiver request
is needed for the non-road portion of the proposed rule.
The commission agrees with the comment and has submitted its waiver request
for the on-road portion of the rules only.
ARTBA, ExxonMobil, Koch, Lyondell-CITGO, Phillips 66, Union Pacific, and
TxOGA commented that the commission failed to follow the requirements for
adopting a major environmental rule as required by Texas Government Code, §2001.0225
(i.e. no cost benefit analysis performed; no draft impact analysis performed;
no description of why identified reasonable alternative were rejected; and
no final RIA performed). BCCA, CITGO, Lyondell-CITGO, Phillips 66, and REI
commented that the proposed rule meets the definition of a major environmental
rule and that the RIA requirements of Texas Government Code, §2001.0225
are triggered because the proposed rule exceeds standards set by federal law
and exceeds an express requirement of state law. BCCA, REI, and Union Pacific
further commented that the commission's efforts to avoid an RIA by asserting
that the proposed rules are exempt from the RIA requirements because federal
law mandates the rules is legally flawed and may render the rules invalid.
UDS commented that the commission is required to perform a RIA since these
proposals will require significant capitol investments by refiners.
The commission agrees with the commenters that the proposed rules meet
the definition of a major environmental rule; however, the commission disagrees
that its interpretation of the exemption for federally mandated standards
is legally flawed. While the rules may require significant capital investments
by refiners, that alone is not enough to trigger the RIA requirements. The
Texas Government Code, §2001.0225 only applies to a major environmental
rule adopted by a state agency, the result of which is to: 1) exceed a standard
set by federal law, unless the rule is specifically required by state law;
2) exceed an express requirement of state law, unless the rule is specifically
required by federal law; 3) exceed a requirement of a delegation agreement
or contract between the state and an agency or representative of the federal
government to implement a state and federal program; or 4) adopt a rule solely
under the general powers of the agency instead of under a specific state law.
This rulemaking action does not meet any of these four applicability requirements,
and is adopted in substantial compliance with the RIA requirements. Texas
Government Code, §2001.035. These rules do not exceed an express standard
set by federal law because the LED requirements are specifically developed
to meet the ozone NAAQS set by the EPA under 42 USC, §7409. Title 42
USC, §7410 requires states to adopt a SIP which provides for "implementation,
maintenance, and enforcement" of the primary NAAQS in each air quality control
region of the state. While 42 USC, §7410 does not specifically prescribe
programs, methods, or reductions to meet the federal standard, state SIPs
must include "enforceable emission limitations and other control measures,
means or techniques (including economic incentives such as fees, marketable
permits, and auctions of emissions rights), as well as schedules and timetables
for compliance as may be necessary or appropriate to meet the applicable requirements
of this chapter" (meaning 42 USC, Chapter 85, Air Pollution Prevention and
Control). The FCAA does require some specific measures for SIP purposes, such
as an inspection and maintenance program, but those programs are the exception,
not the rule, in the federal SIP structure. The provisions of the FCAA recognize
that states are in the best position to determine what programs and controls
are necessary or appropriate in order to meet the NAAQS. This flexibility
allows states, affected industry, and the public, to collaborate on the best
methods for attaining the NAAQS for the specific regions in the state. In
order to avoid federal sanctions, states are not free to ignore the requirements
of 42 USC, §7410, and must develop programs to assure that the nonattainment
areas of the state will be brought into attainment on schedule. Failure to
develop control strategies to demonstrate attainment can result in federal
sanctions. Thus, while specific measures are not prescribed, both a plan and
emission reductions are required to assure that the nonattainment areas of
the state will be able to meet the attainment deadlines set by the FCAA. The
EPA provided the criteria for both the submission and evaluation of attainment
demonstrations developed by states to comply with the FCAA. This criteria
requires states to provide, in addition to other information, photochemical
modeling and an analysis of specific emission reduction strategies necessary
to attain the NAAQS. The commissions photochemical modeling and other analysis
indicate that substantial emission reductions from both mobile and point source
categories are necessary in order to demonstrate attainment. In this case,
this rulemaking is intended to achieve reductions in ozone emissions in the
HGA nonattainment areas. Specifically, as noted elsewhere in these rules preamble,
the emission reductions associated with this rule are a necessary element
of the attainment demonstration required by the FCAA.
This conclusion is supported by the legislative history for Texas Government
Code, §2001.0225. During the 75th Legislative Session, SB 633 amended
the Texas Government Code to require agencies to perform a RIA of certain
rules. The intent of SB 633 was to require agencies to conduct a RIA of major
environmental rules that will have a material adverse impact, and will exceed
a requirement of state law, federal law, or a delegated federal program, or
are adopted solely under the general powers of the agency. The commission
provided a cost estimate for SB 633 that concluded "based on an assessment
of rules adopted by the agency in the past, it is not anticipated that the
bill will have significant fiscal implications for the agency due to its limited
application." The commission also noted that the number of rules that would
require assessment under the provisions of the bill was not large. Because
of the ongoing need to address nonattainment demonstrations required by federal
law, the commission routinely proposes and adopts SIP rules. If each rule
proposed for inclusion in the SIP was incorrectly considered as exceeding
federal law, every SIP rule would require the full RIA contemplated by SB
633. This result would be inconsistent with the cost estimates and fiscal
notes prepared by the commission and by the LBB. Since the legislature is
presumed to understand the fiscal impacts of the bills it passes, and that
presumption is based on information provided by state agencies and the LBB,
the commission believes that the intent of SB 633 was only to require the
full RIA for rules that meet the requirements under §2001.0225(a). While
the SIP rules will have a broad impact, that impact is no greater than is
necessary or appropriate to meet the requirements of the FCAA. In other words,
the proposed rules are intended to meet federal and state law, and do not
go above and beyond what is required to meet federal or state statutes.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
It is presumed that "when an agency interpretation is in effect at the time
the legislature amends the laws without making substantial change in the statute,
the legislature is deemed to have accepted the agency's interpretation."
The commission's interpretation of the RIA requirements is also supported
by a change made to the APA by the legislature in 1999. In an attempt to limit
the number of rule challenges based upon APA requirements, the legislature
clarified that state agencies are required to meet these sections of the APA
against the standard of "substantial compliance." Texas Government Code, §2001.035.
The legislature specifically identified §2001.0225 as falling under this
standard. The commission substantially complied with the requirements of §2001.0225.
Therefore in addition to not exceeding an express standard set by federal
law, these rules does not exceed state requirements, and are not adopted solely
under the general powers of the agency because the provisions of the TCAA, §§382.011,
382.012, 382.017, 382.019, 382.037(g), and 382.039 authorize the commission
to implement a plan for the control of the states air quality, including measures
necessary to meet federal requirements. The remaining applicability criteria,
pertaining to exceeding a delegation agreement or contract between the state
and the federal government does not apply. Thus, the commission is not required
to conduct a regulatory analysis as provided in Texas Government Code, §2001.0225.
ExxonMobil and Union Pacific commented that the proposed rules were proposed
without adequate notice as required by Texas Government Code, §2002.024.
The commenters stated that Texas Government Code, §2001.024, requires
adequate notice of a proposed rule, including information about its public
benefits and costs. The commenters stated that adequate notice is essential
for fairness as well as a meaningful opportunity to comment on a proposed
rule, and that courts have considered notice "adequate" only if: interested
persons can confront the agency's factual suppositions and policy preconceptions;
and the agency provides interested parties the opportunity to challenge the
underlying factual data relied upon by the agency. The commenters asserted
that the proposal included insufficient information and analysis regarding
costs and impacts. The commenters asserted that in proposing the rules, the
commission failed to provide interested parties with sufficient information
to constitute adequate notice.
The commenters stated that it has identified a number of critical gaps
in the underlying factual data, methodology, and analysis in support of the
proposed rules. The commenters asserted that the commission has not adequately
responded to requests for additional information from stakeholders. The commenters
stated that the following requests for information were outstanding: information
regarding the modeling of emissions; information regarding the corrected emissions
inventory database; and information supporting the estimated costs of control.
The commenters stated that this information is necessary in order to comment
effectively on the proposed rules and that data gaps in the proposal hindered
effective comment.
The commission disagrees with the commenters and made no change in response
to these comments. Texas Government Code, §2001.024 requires of the notice
of a proposed rule include certain information. Subsection (a)(5) requires
that the notice state the public benefits expected as a result of the adoption
of the proposed rule and the probable economic cost to persons required to
comply with the rule. Adequate notice is essential for fairness as well as
a meaningful opportunity to comment on a proposed rule.
United Loans, Inc. v. Pettijohn,
955 S.W.2d 649, 651 (Tex. App - Austin
1997). To achieve the goal of encouraging meaningful public participation
in the formulation and adoption of rules by state agencies, the notice must
have sufficient information so that interested persons can determine whether
it is necessary for them to participate in order to protect their legal rights
and privileges. The proposed rules contained an analysis of information available
to the commission regarding the costs and benefits of the proposed rules.
The commission received intelligent comments which were substantial in both
number and in scope, regarding the costs as well as the benefits. Therefore,
the commission believes this goal has been achieved and that the notice includes
sufficient information to constitute adequate notice.
The purpose of the comment period is for the public to provide the commission
with information to say why they agree or disagree. There is no requirement
that the commission determine the probable economic cost of the unique aspects
of every facility or source that must comply, nor give the probable economic
cost of every possible method of control. Rather, the notice must include
the cost of a reasonable method of compliance. Mere disagreement with cost
estimates does not render notice inadequate.
The proposed rules meet the requirement to include sufficient information
explaining the fuel concentration requirements, to whom they apply, the compliance
schedule, the anticipated cost of compliance, and the anticipated reduction
in emissions. To simply state that the proposal failed to provide sufficient
information does not provide the commission with sufficient information to
propose changes or alternative strategies. The commenters did not say how
the notice is insufficient, merely that it is insufficient. Nevertheless,
the commission reviewed the notice, determined it to be adequate, and responded
to comments regarding costs associated with compliance with these rules elsewhere
in this ANALYSIS OF TESTIMONY.
Similarly, the comments which state there are critical gaps did not identify
what those gaps are or how that results in inadequate notice. The commission
is unaware of any requests for additional information to which it was not
completely responsive.
BCCA, ExxonMobil, Lyondell-CITGO, Phillips 66, REI, and Union Pacific commented
that the commission proposed these rules without an adequate TIA as required
by Texas Government Code, §2007 and that, although the commission asserted
an exemption from performing a TIA based on the assertion that the proposal
does not impose a greater burden than necessary to advance a health and safety
propose and that the proposal "reasonably" fulfills federal mandates, the
commission failed to provide the public a basis to infer that a cost/benefit
analysis or a reasonableness determination was, in fact, performed as necessary
to support the commission's exemption claim. The commenters stated that the
TIA provision mandates that covered agencies "take a 'hard look' at the private
real property implications of the actions they undertake . . . ," according
to the Office of the Attorney General,
Private Real
Property Rights Preservation Act Guidelines,
(21 TexReg 387, January
12, 1996). The commenters stated that under §2007.043, a TIA must describe
the specific purpose of the proposed action, determine whether engaging in
the proposed governmental action will constitute a taking, and describe reasonable
alternative actions that could accomplish the specified purpose. The commenters
stated that the agency must also explain whether these alternative actions
also would constitute takings.
The commenters stated that agencies must also comply with guidelines developed
by the Texas Attorney General when developing the TIA and that according to
these guidelines, agencies must carefully review governmental actions that
have a significant impact on the owner's economic interest. The commenters
stated that these guidelines include the statement: "Although a reduction
in property value alone may not be a 'taking,' a severe reduction in property
value often indicates a reduction or elimination of reasonably profitable
uses." (21 TexReg 392, January 12, 1996).
The commenters stated that the proposed rule preamble acknowledged that
some of the rules may "burden" private real property, including these rules,
but claimed an exemption from performing a TIA based on the assertion that
the proposal does not impose a greater burden than necessary to advance a
health and safety purpose and that the proposal "reasonably" fulfills a federal
mandate. The commenters stated that the commission provided the public no
basis to infer that a cost/benefit analysis or a reasonableness determination
was, in fact, performed as necessary to support the TIA exemption claim because
the preamble contains only the bare assertions. The commenters asserted that
the proposed rules will impose a greater burden than is necessary, and are
not reasonably taken to fulfill a federal mandate. The commenters believed
that according to the Attorney General's Guidelines, a full TIA was required
to be completed with the proposal, and that failure to perform a TIA could
invalidate the rules.
As stated previously in the preamble, the purpose of the adopted rules
is to ensure that LED is in place for all areas of the state in order to conform
with the air quality standards established under federal law as NAAQS for
ozone. The commission noted in the proposal that the rules may require the
installation of control systems at refineries in some cases. The acknowledgment
that the rules may require a capital investment or the installation of controls,
is simply that, an acknowledgment. The commission understands that the rules
may have an impact on real property and in noting this, sought comments on
any potential impact to ensure that the adopted rules are technically and
economically feasible. The commission believes that this acknowledgment has
caused the commenters to misunderstand the commission's interpretation of
the requirements of Texas Government Code, Chapter 2007. The commission does
not believe that the assessment required by Chapter 2007 begins with a determination
of whether or not the proposed rules could result in a capital investment.
Rather, the commission believes that before an assessment is required, the
commission must determine whether Chapter 2007 applies to the government action.
If the proposed action is subject to an exception to Chapter 2007, the analysis
is complete. Section 2007.003(b) provides that "this chapter does not apply
to the following governmental actions. . . ." Because the commission believes
the adopted rules meet the two exceptions to Chapter 2007, the full TIA is
not required for the rules.
The commission believes the adopted rules are exempt under Texas Government
Code, §2007.003(b)(4) because they are reasonably taken to fulfill an
obligation mandated by federal law. While several governmental actions are
subject to being reviewed under Chapter 2007, including the adoption of rules, §2007.003(b)(4)
specifically excludes an action that is reasonably taken to fulfill an obligation
mandated by federal law. The purpose of this rulemaking is to meet the air
quality standards established under federal law as NAAQS.
The commission also believes that the adopted rules meet an additional
exception to the requirements of Texas Government Code, Chapter 2007. First,
Texas Government Code, §2007.003(b)(13), states that Chapter 2007 does
not apply to an action that: 1) is taken in response to a real and substantial
threat to public health and safety; 2) is designed to significantly advance
the health and safety purpose; and 3) does not impose a greater burden than
is necessary to achieve the health and safety purpose. Although the rule revisions
do not directly prevent a nuisance or prevent an immediate threat to life
or property, they do prevent a real and substantial threat to public health
and safety and significantly advance the health and safety purpose. This action
is taken in response to the HGA area exceeding the federal ambient air quality
standard for ground-level ozone, which adversely affects public health, primarily
through irritation of the lungs. The action significantly advances the health
and safety purpose by reducing ambient VOC and ozone levels in HGA. Consequently,
these rules meet the exemption in §2007.003(b)(13).
The commission has included elsewhere in this preamble its reasoned justification
for adopting this strategy and has explained why it is a necessary component
of the SIP which is federally mandated. This discussion, as well as the HGA
SIP which is being adopted concurrently, explains in detail that every rule
in the HGA SIP package is necessary and that none of the reductions in those
packages represent more than is necessary to bring the area into attainment
with the NAAQS. This rulemaking therefore meets the requirements of Texas
Government Code, §2007.003(b)(4) and (13). For these reasons the rules
do not constitute a takings under Chapter 2007 and do not require additional
analysis.
BCCA, ExxonMobil, Lyondell-CITGO, Phillips 66, REI, and Union Pacific commented
that the commission proposed these rules without an adequate small and micro-business
assessment as required by Texas Government Code, §2006.002 and that it
is not sufficient for the commission to merely state that the costs for small
and large businesses with be the same or that the costs to small businesses
cannot be determined, but that the commission is required to provide a cost
comparison using an established standard to determine whether there is a disparate
impact on small business. BCCA and REI further added that the commission did
not publish the information mandated by Texas law and as a result, it is impossible
for the public to comment on whether the commission adequately considered
the effect of the proposed rules on small businesses.
The agency has estimated, to the extent possible, the costs to small businesses
and has determined that the cost depends more upon the amount of diesel fuel
consumed by the business and that it is not dependent upon the number of employees,
hours of labor, or amount of sales income. Some small businesses use large
amounts of diesel fuel while other use none. Large businesses vary in the
same way. The commission provided the estimated cost per gallon of fuel and
argues that this is the only meaningful way to provide sufficient notice of
the cost to small business and therefore that it meets the objective of the
Texas Government Code, Chapter 2006. This assertion is supported by the fact
that no small businesses provided comments which include cost of compliance
in terms of the number of employees, hours of labor, or amount of sales income.
BCCA, ExxonMobil, Lyondell-CITGO, Phillips 66, REI, and Union Pacific commented
that the commission proposed these rules without a Local Employment Impact
Statement as required by Texas Government Code, §2001.022 and that the
commission failed to make the required initial determination, apparently ignoring
that there is a great potential for the proposed rules to adversely affect
the local economy.
The commission agrees with the commenters that the proposed rules may affect
a local economy, however, does not agree that it is the responsibility of
the commission to provide the local employment impact analysis. The APA requires
state agencies to determine whether a rule may affect a local economy before
proposing a rule for adoption. If the agency determines that a proposed rule
may affect a local economy, the agency must send a copy of the proposed rule
and other information to the Texas Workforce Commission (Workforce Commission)
before the agency files notice of the proposed rule with the secretary of
state. The APA requires the Workforce Commission to prepare a local employment
impact statement for proposed rules, if a state agency requests the statement.
The commission determined that the proposed rules might affect a local economy,
and sent the proposed rules and other requested information to the Workforce
Commission. The commission received a letter from the Workforce Commission,
indicating that the Workforce Commission did not have the ability to determine
the potential local employment impacts from the proposed rules.
BCCA, Koch, Lyondell-CITGO, REI, Phillips 66, and TxOGA commented that
the proposed fuel rule is specifically prohibited by the Texas Health and
Safety Code, §382.037(g) which prohibits state regulation of fuel content
to a level more stringent than required by federal law unless a determination
is made that a more stringent fuel-content rule is necessary to meet the ozone
NAAQS. Phillips 66 and TxOGA further added that this prohibition would especially
apply toward the attainment areas proposed to be affected by the proposal.
BCCA and REI added that the commission therefore lacks the authority to require
fuel controls in attainment areas. ExxonMobil commented that the commission
must resolve several legal issues including the commission exceeding federal
requirements without justification and the lack of financial and risk assessments
as required by state law.
Texas Health and Safety Code, §382.037(g) authorizes the commission
to regulate fuel content under certain circumstances, including the situtation
where the regulation is necessary for the attainment of the federal ozone
ambient air quality standards. In its request for a federal waiver from the
EPA, the commission demonstrates that the rules are a necessary component
of the SIP and that there are no other reasonable or practicable alternatives
available. This demonstration applies statewide and also satisfies the condition
of §382.037(g) that the rules are necessary to meet the NAAQS.
ExxonMobil commented that the commission has not provided valid and adequate
scientific and technical analysis or justification, nor legal justification
for the proposed 2004 implementation schedule, which exceeds federal requirements.
The commission revised the rule to delete the proposed requirements which
would have required 30 ppm sulfur by May 1, 2004 in order to provide greater
flexibility for producers to comply with these rules and to be consistent
with anticipated federal rulemaking and implementation schedules.
Phillips 66 and TxOGA commented that the proposed rules violate FCCA, §211(c)
which is a federal preemption of state regulation of fuel content to more
stringent level than as regulated by the EPA unless a waiver has been applied
for and approved in the SIP. Phillips 66 and TxOGA further added that the
commission simply made conclusory statements about the need to control NO
The commission is approving simultaneously with these rules a SIP submittal
which includes a FCAA, 211(c)(4)(C) waiver request and demonstration. This
submittal includes all required components including a justification for the
area of coverage. The commission is confident that the submittal meets the
requirements for such a waiver and that the waiver will be approved by the
EPA.
Baker Botts, BCCA, Dynegy, Dow, ExxonMobil, and Union Pacific commented
that since EPA-regulated sources account for about 40% of the NO
x
emissions in the affected areas, and that these sources are federally
preempted and only the EPA, not the state, can effectively regulate them,
the commission should incorporate an appropriate level of "federal assignments"
into the proposal to restore it balance and to address the proposal's undue
reliance on state-regulated sources. The commenters stated that the EPA issued
a number of regulations for some federally preempted sources, such as land-based
spark engines, marine, recreational and land-based diesel engines, aircraft
and locomotive engines, well after the FCAA deadlines, and that the EPA recently
strengthened rules for on-road and non-road vehicles and fuels, such as low
sulfur gas and diesel, Tier II motor vehicles, heavy-duty highway vehicle
standards, and non-road Tier II/Tier III heavy-duty engine standards. The
commenters stated that delays in implementing these rules have prompted the
commission to propose technically and economically infeasible emission reductions
from sources in HGA that the state has authority to regulate to make up for
the missing federal reductions. The commenters stated that these delays have
forced the commission to propose expensive regional fuels and significant
use restriction regulations. The commenters stated that the commission and
the EPA can ensure an equitable distribution of the compliance burdens necessary
to meet mandated air quality improvement in HGA only by allowing the SIP to
capture anticipated emission reductions from federally preempted sources.
Baker Botts noted that the EPA demonstrated a willingness to assume responsibility
for a portion of emission reductions by creating a process in Los Angeles
called a "public consultative process," that would resolve issues related
to emissions from national and international sources, and that the EPA has
also provided flexibility in obtaining offsets by allowing states to provide
offsets to refiners based on emission reductions that the EPA projected would
result from mobile sources using Tier II gasoline. Baker Botts suggested that
this same sort of prospective crediting should be used to develop a more rational
HGA SIP, and that the EPA should allow the commission to credit in the SIP
the prospective emission reductions that will result from implementation of
the Tier II gasoline rule and from other federally preempted sources. Finally,
Baker Botts cited two cases wherein the District of Columbia Circuit has approved
the EPA flexibility with respect to statutory deadlines under the FCAA when
the EPA has failed to meets its own deadlines, and this failure was deemed
to upset the balanced federal/state responsibilities under the FCAA. ExxonMobil
commented that it supports the commission and the EPA crediting the HGA SIP
with an additional 60 tpd of federally preempted emission reductions that
will occur over the next ten years. Harris County commented that the commission
should work with the EPA to accelerate the implementation schedule for federally
preempted emissions so that at least one-half of the related emission reductions
are achieved by 2007, and that as a part of this process, the commission should
delineate federal assignments detailing the engine standards and emission
reductions necessary to achieve real and sustainable pollution reductions.
The commission agrees with the commenters that emission reductions from
federally preempted sources would provide benefits for the HGA SIP demonstration,
and the inability of the commission to regulate certain source categories
has necessitated the use of other ozone control strategies. However, the commission
understands that the EPA SIP approval process does not provide a mechanism
for credit for emission reductions that occur after the attainment date. The
commission understands that the EPA is not currently considering accelerating
implementation schedules for existing federal rules. The commission is working
with the EPA to determine the availability of SIP credit for many non-traditional
control strategy mechanisms, like economic incentive programs and flexibility
for preempted source categories. Additionally, the commission is working with
the EPA to determine an appropriate federal contribution credit available
for the HGA SIP.
Lyondell-CITGO, Phillips 66, and TxOGA commented that the proposed rules
are being promulgated under improper rulemaking procedures due to the lack
of a reasoned justification for the rules as required by Texas Government
Code, §2001.033(a) and that the commission has not provided a reasonable
justification for the application of the proposed rule in attainment areas.
Phillips 66 and TxOGA further added that the FCAA evidences a clear congressional
purpose to have nonattainment areas bear the economic burdens and sanctions
of not being in compliance with NAAQS and that the commission is superceding
this principle by seeking a regional solution to local nonattainment conditions.
TMTA and Koch commented that the commission does not have the authority to
require cleaner diesel fuel beyond the nonattainment area and requested that
the commission identify the regulatory authority under which it is requiring
cleaner diesel fuel in attainment counties.
The commission adopts these rules pursuant to authority TCAA, §§382.011,
382.012, 382.017, 382.019, 382.037(g), and 382.039. The underlying reason
for adopting the rules is that they are necessary to achieve and to maintain
attainment in the State of Texas especially in the nonattainment areas and
the near nonattainment areas. The authority cited is not limited to nonattainment
areas. As noted in the rule preamble, the commission expanded the rules to
cover the entire state as a means to help alleviate concerns regarding out-of-area
refueling practices in relation to the nonattainment counties and to reduce
the regional transport of ozone precursors. Federal and state studies have
shown that pollution from one area can affect ozone levels in another area.
This work is supported by the findings of the OTAG study, which is the most
comprehensive attempt ever undertaken to understand and quantify the transport
of ozone. Both the commission and the OTAG study results point to the need
to take a regional approach to control air pollutants, such as that prescribed
in the rules. The state-wide implementation of LED fuel will help reduce the
amount of NO
x
being transported into the HGA,
BPA, and DFW ozone nonattainment areas and other areas of the state having
concerns over air quality. The state-wide coverage will also provide a greater
market for diesel fuel producers and importers to provide the fuel required
by these regulations. The commission and local area evaluated over 250 possible
strategies while developing the attainment demonstration. These were identified
in Appendix L of the SIP submittal. Modeling assessing the benefits of these
rules demonstrated that by the year 2007, the use of LED will reduce NO
The commission has demonstrated in the SIP that these rules are necessary
to achieve the NAAQS. The commission disagrees with the comment that these
rules circumvent the intent of Congress to limit the burden of non-compliance
with the NAAQS to those areas specifically designated nonattainment. If Congress
had intended SIP strategies to be implemented only in nonattainment areas
it could have specified so in the FCAA. And if Congress intended a fuel waiver
request only to be granted for implementation in nonattainment area it could
have specified so in FCAA, §211(c)(4)(C). However, Congress used the
broad language allowing waivers of federal preemption if the fuel strategy
"is necessary to achieve the national primary or secondary ambient air quality
standard which the plan implements." Congress did provide additional limitation
to this waiver, although they do not limit the waiver as far as the commenters
suggest. The additional limitation has to do with whether there are other
reasonable and practicable measures which can be used instead. The commission
has fulfilled all of the limitations which Congress placed on the waiver of
federal preemption for fuel strategies and has demonstrated this in its SIP
submittal. Therefore, the commission disagrees that this strategy circumvents
the intent of Congress.
CBC, KIMI, Suderman, TWOA, and WTC commented that the commission lacks
authority to regulate tug/towboat sources under the Commerce Clause of the
United States Constitution and federal preemption of marine vessels as non-road
mobile sources. TWOA further added that the commission lack authority under
Texas Health and Safety Code, §382.019(a) to regulate marine vessels
and engines since this regulation is specific to engines used to propel land
vehicles.
The commission disagrees that the rules are preempted as regulations of
non-road mobile sources. The commission points out that the regulated entities
under these rules are the suppliers of diesel fuel, not the users. These rules
do not require anything of tug/towboat sources. The commenter's interpretation
of §209(e) would contradict the clear authority under §211(c)(4)(C)
for states to adopt fuel regulations under certain circumstances. Therefore,
these rules are not preempted as non-road engine standards.
The rules do not violate the Interstate Commerce Clause for a number of
reasons. The rules do not impose different burdens on out-of-state entities,
they do not impose any requirement on the equipment operator, either directly
or indirectly, and they do not actually regulate what fuel may be used, only
what fuel is available for sale. These rules will not require marine vessels
to have different equipment to operate in Texas. The rules do not regulate
the design, construction, alteration, repair, maintenance, operation, equipping,
personnel qualification, and manning of marine vessels. The rules promulgated
by the commission are specifically designed to attain a federal standard which
applies equally in all states. Texas must comply with these limits like all
states, and in so doing must choose which sources to regulate. The commission's
actions do not place burdens on interstate commerce, they simply regulate
local activities within the H/GA area, and thus do not violate the Commerce
Clause of the United States Constitution.
Although the commission disagrees that there is any burden placed on interstate
commerce by these rules and the corresponding SIP, any burdens that might
be found are merely incidental and thus the regulations are allowable exercises
of the state's police powers to promote health and safety. The United States
Supreme Court has consistently held that the Commerce Clause is not an absolute
bar to state regulation. "The limitation imposed by the Commerce Clause on
state regulatory power is by no means absolute, and the states retain authority
under their general police powers to regulate matters of legitimate local
concern, even though interstate commerce may be affected."
Maine v. Taylor,
477 U.S. 131, 138 (1986)
citing Lewis v. BT Investment Managers, Inc.,
447 U.S. 27, 36 (1980).
The Court has also consistently ruled that states may impose incidental burdens
on interstate commerce, so long as the burdens are not "clearly excessive
in relation to the putative local benefits."
Pike
v. Church,
397 U.S. 137 (1970). It has also been held that "{t}he protection
of the environment and conservation of natural resources . . . are areas of
legitimate local concern" justifying incidental burdens on interstate commerce.
Finally, Texas Health and Safety Code, §382.019 specifically authorizes
rules to reduce emissions from engines used to propel land vehicles. Engines
which use fuel subject to these rules are used, at least in part, to propel
the equipment. The statute doesn't limit the commission's authority to control
emissions from engines which are used solely or primarily to propel engines.
Therefore the commission asserts that §382.019 does provide authority
for the adoption of these rules. Additionally, the presence of this authorization
does not imply a lack of authority to control emissions from other types of
vehicles or equipment. For these reasons, the commission disagrees that this
rulemaking exceeds its statutory authority.
KIMI, Suderman, and WTC commented that the commission proposed regulations
that adversely affect their equipment while at the same time poses a direct
threat to the safety of its operations and that the commissions should specifically
exempt tug and tow boats from all proposed regulations because the proposed
rules impose standards that unreasonably interfere with interstate commerce
and impose an uniquely local standard in violation of the federal government's
intent to regulate the maritime industry and under the Commerce Clause and
require tug and tow boats to use unproven technology and fuel which could
create a significant risk of substantial marine casualty and a threat of adverse
impact to the environment and health and safety of the crew and surrounding
population.
The control strategies being implemented by the commission in the HGA nonattainment
area are necessary to the area's federal requirement to demonstrate attainment
by 2007 and all possible reductions are needed. The commission believes that
tug/tow boats are a contributing emission source in the HGA area and that
it would not be appropriate to exclude them from these rules. As previously
mentioned, the commission does not have any evidence to support the assertion
that the LED fuel will adversely affect the commenters' equipment.
These rules do not directly apply to the user of the fuel but to the supplier.
The rules simply regulate which fuel is available to those who purchase it
in the state. Marine vessels which travel interstate are free to obtain fuel
outside the state. For the reasons mentioned in a previous response, these
rules do not violate the Interstate Commerce Clause. Additionally, these rules
are not a regulation of the maritime industry.
ARTBA commented that the state is preempted under FCAA, §209(e) from
adopting or attempting to enforce any standard or other requirement relating
to the control of emissions from new farm or construction vehicles or engines
under 176 hp or locomotives and as such the proposed fuel rules are not legally
defensible.
The commission disagrees with the commenter's interpretation of FCAA, §209(e).
This statutory provision is aimed at preventing manufacturing standards for
new engines. See
Engine Manufacturers Association
v. EPA,
88 F.3d 1075, 1079 (D.C. Cir. 1996). Under the court's interpretation,
only standards which apply to the non-road vehicles or engines are preempted
by §209(e). States retain authority to promulgate in-use restrictions.
Under this rule, no manufacturer will have to create a special vehicle for
Texas which is what Congress intended to prohibit. The commenter's interpretation
of §209(e) would contradict the clear authority under §211(c)(4)(C)
for states to adopt fuel regulations under certain circumstances.
DoD commented that military equipment and fuel used to power the equipment
should be exempted from these proposed rules under FCAA, §203(b)(1) and
under the definition of motor vehicles specified in 40 CFR §85.1703 and
under the exemption allowed in §85.1708 to exempt tactical wheeled vehicles
from meeting the new 2007 emission standards.
DoD requested that the commission add a new subsection (c) to §114.317
which states as follows:
Equipment, which may otherwise be subject to this
chapter, but used by any Department of Defense component, (including but not
limited to the Departments of the Army, Navy, Air Force, any Reserve Component
or National Guard Entity), and powered by a fuel in accordance with DoD mission
requirements and directives shall not be subject to the requirements of this
chapter.
The commission disagrees with this comment. The commission believes that
this exemption is not needed as the definition for diesel fuel as specified
in §114.6 precludes the fuel normally used by the DoD in its vehicles
and engines, specifically JP-5 and JP-8. The commission made no change to
the rule language in response to this comment.
Union Pacific expressed concern that the definition of "importer" could
be read to include a railroad acting in its capacity as a common carrier of
freight, i.e. merely hauling tank cars filled with diesel fuel into the HGA
area while under hire by a separate entity, and requested that the commission
provide a clarification in the rule that does not require common carriers
to ensure that the fuel they haul meets the requirements of this rule. TPCA
commented that transporters should not be considered "importers" because they
have no control over the fuel they transport beyond moving the fuel from one
destination to another at the behest of a supplier and that recordkeeping
and reporting requirements should only be applied to those entities exercising
control over the fuel's characteristics such as refiners manufacturing fuel
for sale inside the state of Texas. TxOGA supported the proposed changes to
the definitions of import and importer.
The commission agrees with this comment and made clarifications to the
rule to exempt common carriers and transporters from the registration, reporting,
and recordkeeping requirements by adding new definitions for transport and
transporter and revising the definition of importer to exclude transporters
acting in their capacity as common carriers.
TPCA recommended that the definition of "importer" be amended to apply
to only those persons who import motor vehicle fuel into the affected counties
listed in §114.319.
The rule requires diesel fuel to meet the LED requirement statewide in
2002 and as such the definition of importer must cover all persons who import
fuel into the state. The commission made no change to the rule language in
response to this comment.
Koch expressed concern that since the EPA made it clear that they consider
ultra-low sulfur diesel fuel (in conjunction with advanced technology after-treatment)
to be the only fuel reformulation approach that they consider cost effective
or appropriate, the test protocol prescribed in 30 TAC §114.315(c) for
alternative diesel formulation approval would be the only viable protocol
acceptable by the EPA and therefore there would be no alternative to major
refinery and infrastructure modification to comply with the proposed diesel
fuel rule.
As noted in the rule preamble, the rules do allow the use of alternative
formulations that provide the same emissions performance as the specified
fuel content standards for aromatics and cetane. The commission believes that
producers should be able to provide these alternative formulations in sufficient
quantities in the near term to alleviate any concerns over the availability
of supply for the 2002 implementation date. The alternative formulations may
be produced through existing refining practices or through the use of additives
as long as the emissions performance is equivalent to the specified fuel standards.
As such, if alternative formulations are used, producers should be able to
begin supplying diesel fuel compliant to the rules within the specified time
frame. In addition, the commission believes that new refining technologies
for reducing sulfur, such as the recently introduced Phillips 66 "S Zorb"
technology and BP's OATS process, could significantly reduce production costs
and could help alleviate concerns over supply availability. The EPA rulemaking
regarding federal sulfur requirements does not imply that there are not areas
of the nation that need more stringent controls. The commission submitted
a request to the EPA for a waiver under FCAA, §211(c)(4)(C) which demonstrates
the need for these rules. The commission believes that the waiver requirements
have been met and anticipates that the EPA will approve the waiver. The commission
made changes to the rules in response to these comments to include additional
flexibility for approval of alternative diesel fuel formulations which are
intended only for use in non-road equipment.
The EPA commented that §114.315(c) was not clear on whether alternative
diesel fuel formulations would be approved with sulfur level greater than
30/15 ppm sulfur and if they are, these formulations could cause enforcement
problems by contaminating supplies of compliant diesel fuel when mixed in
retail storage tanks and therefore the proposed rule should require retailers
and distributors to maintain all records relevant to fuel deliveries, including
daily stick readings and meter readings to be maintained, and requiring stick
readings before and after every fuel delivery to be maintained. The EPA commented
that §114.315(c)(4) does not seem to require the applicant to show the
effects of using a product that consists of commingled candidate fuel and
referenced fuel and that this raises technical concerns about the effectiveness
of alternative diesel fuel formulations, if not segregated from 30/15 ppm
fuel at all parts of the distribution system.
The commission agrees that the rule proposal was not clear as to the commission's
intent that all alternative diesel fuel formulations approved under §114.315(c)
be required to meet the sulfur standards as specified in §114.312(b)
and that the alternative formulations were only intended for compliance flexibility
with the aromatic and cetane standards as specified in §114.312(c) and
(d). The commission made clarifying changes to §114.312(g) to specify
that the sulfur standard is not covered under the alternative formulation
provisions of §114.315(c), only the aromatic and cetane standards.
The EPA commented that the proposed rules should require alternative diesel
fuel formulations to be segregated from 30/15 ppm diesel in terminal storage
tanks, as well as at retail level, in order to make the proposed rules enforceable.
The EPA commented that the definitions of import facility and importer do
not necessarily facilitate allowing the commission to track fuel from a refinery
to a particular import facility without a requirement to designate and segregate
every batch of fuel produced by each refinery, especially batches of alternative
diesel fuel formulations with sulfur levels exceeding 30/15 ppm sulfur, and
that without such a requirement the alternative diesel fuel formulation will
be treated by pipelines and terminal as fungible 30/15 ppm product and commingled
with LED from other refineries resulting in contamination of the compliance
fuel with sulfur levels exceeding the sulfur standard.
The commission made changes to the rule language based on the previous
comment that no longer allows the sulfur level of the alternative formulation
to deviate from the specified sulfur standard. Therefore, both alternative
formulations and compliance diesel fuel will be required to meet the same
sulfur standard and there will be no need to segregate the alternative formulation
from other compliance diesel within the distribution system.
The EPA commented that in 30 TAC §114.315(c) the commission should
set upper and lower limits to all relevant specifications when approving alternative
diesel fuel formulations, especially for sulfur content.
The commission disagrees with this comment. The rule allows the use of
alternative formulations that provide the same emissions reduction performance
as the specified LED fuel as flexibility for producers in complying with the
aromatic and cetane standards. Upper and lower limits are not required for
alternative formulations since all diesel must continue to meet the minimum
requirements for federal diesel fuel in order to be used on-road in Texas.
As mentioned previously, the alternative formulation provision has been clarified
to specify that it does not cover sulfur content. The commission made no changes
in response to this comment.
The EPA commented that the commission should clarify the definition for
bulk plant which seems to include all terminals and asked whether this was
intended.
The commission believes that the definition of bulk plant is clearly understood
to include terminals and that it was the commission intent to include these
facilities under these regulations. The commission made no change to the rule
language in response to this comment.
The EPA commented that it does not understand the difference between the
terms, "producer" and "refiner," and asked whether it is the intent to make
"refiners" a subset of the term, "producer."
The commission agrees with this comment in that there seemed to be no difference
in the coverage of the terms, "producer" and "refiner," in the rule proposal.
The commission made changes in the rule language to remove the definitions
for refiner and refinery and incorporate their meaning into the definitions
of producer and production facility and also make clarifying changes through
the rules to reflect these revisions.
The EPA commented that the language in §114.314 is confusing since
the person who imports the fuel is not necessarily the same person who stores
the fuel in a fixed storage facility and therefore the term, "its facility,"
as used in conjunction with the term, "importer," will frequently not apply.
The commission disagrees with this comment. The definition of import facility
in §114.6 does not specify whether the import facility has to be owned
or operated by the importer, only that it is where the importer takes delivery
of the imported fuel and from which this fuel is transferred into the distribution
system. Therefore, the language in §114.314 will always apply to the
importer regardless of whether the importer is the same person that originally
stored the fuel at that facility. The commission made no change to the rule
language in response to this comment.
The EPA commented that the commission does not appear to have included
a test method for sulfur in §114.315.
The test method for sulfur is specified in §114.315(a)(1) as adopted
by the commission on April 19, 2000. The commission made no changes in the
rule language in response to this comment.
Subchapter A. DEFINITIONS
30 TAC §114.6
STATUTORY AUTHORITY
The amendment is adopted under TWC, §5.103, which authorizes the commission
to adopt rules necessary to carry out its powers and duties under the TWC;
and under the Texas Health and Safety Code, TCAA, §382.017, which authorizes
the commission to adopt rules consistent with the policy and purposes of the
TCAA. The amendments are also adopted under TCAA, §382.011, which authorizes
the commission to control the quality of the state's air; §382.012, which
authorizes the commission to prepare and develop a general, comprehensive
plan for the control of the state's air; §382.019, which authorizes the
commission to adopt rules to control and reduce emissions from engines used
to propel land vehicles; §382.037(g), which authorizes the commission
to regulate fuel content if it is demonstrated to be necessary for attainment
of the NAAQS; and §382.039, which authorizes the commission to develop
and implement transportation programs and other measures necessary to demonstrate
attainment and protect the public from exposure to hazardous air contaminants
from motor vehicles.
§114.6.Low Emission Fuel Definitions.
Unless specifically defined in the TCAA or in the rules of the commission,
the terms used in this subchapter have the meanings commonly ascribed to them
in the field of air pollution control. In addition to the terms which are
defined by the TCAA, §3.2 of this title (relating to Definitions), and §101.1
of this title (relating to Definitions), the following words and terms, when
used in Subchapter H of this chapter (relating to Low Emission Fuels), shall
have the following meanings, unless the context clearly indicates otherwise.
(1)
Additive - Any substance, other than one composed solely
of carbon and/or hydrogen, that is intentionally added to gasoline or diesel
fuel, including any added to a motor vehicle fuel system, and that is not
intentionally removed prior to sale or use and that is approved by and registered
with the EPA in accordance with 40 Code of Federal Regulations 79.
(2)
Barrel - A unit of measure equal to 42 United States gallons.
(3)
Bulk plant - An intermediate motor vehicle fuel distribution
facility where delivery of motor vehicle fuel to and from the facility is
solely by truck or pipeline.
(4)
Bulk purchaser/consumer - A person who purchases or otherwise
obtains motor vehicle fuel in bulk and then dispenses it into the fuel tanks
of motor vehicles owned or operated by the person.
(5)
Common carrier - A person engaged in the transportation
of goods or products of another person for compensation and is available to
the public for hire.
(6)
Designated alternative limit (DAL) - An alternative specification
limit for a specific fuel standard, which is assigned by a producer or importer
to a final blend of low emission diesel fuel (LED) in accordance with §114.313
of this title (relating to Designated Alternative Limits).
(7)
Diesel fuel - Any fuel that is commonly or commercially
known, sold, or represented as diesel fuel Number 1-D or Number 2-D, in accordance
with the American Society for Testing and Materials (ASTM) Test Method D975-98b
(Standard Specification for Diesel Fuel Oils), dated 1998.
(8)
Final blend - A distinct quantity of LED which is introduced
into commerce without further alteration which would tend to affect a regulated
LED specification of the fuel.
(9)
Further process - To perform any activity on motor vehicle
fuel, including distillation, treating with hydrogen, or blending, for the
purpose of bringing the motor vehicle fuel into compliance with the requirements
of Subchapter H of this chapter.
(10)
Gasoline - Any fuel that is commonly or commercially known,
sold, or represented as gasoline, in accordance with ASTM Test Method D4814-99
(Standard Specification for Automotive Spark-Ignition Engine Fuel), dated
1999.
(11)
Import - The process by which motor vehicle fuel is transported
into the State of Texas by any means or method whatsoever, including transport
via pipeline, railway, truck, motor vehicle, barge, boat, or railway tank
car.
(12)
Import facility - The stationary motor vehicle fuel transfer
point wherein the importer takes delivery of imported motor vehicle fuel and
from which imported motor vehicle fuel is transferred into the cargo tank
truck, pipeline, or other delivery vessel from which the fuel will be delivered
to a bulk plant or retail fuel dispensing facility.
(13)
Importer - Any person, except a person acting as a common
carrier, who imports motor vehicle fuel.
(14)
Low emission diesel (LED) - Any diesel fuel:
(A)
sold, intended for sale, or made available for sale which
may ultimately be used to power a diesel fueled compression-ignition engine
in the counties listed in §114.319 of this title;
(B)
that the producer knows, or reasonably should know, may
ultimately be used to power a diesel fueled compression-ignition engine in
counties listed in §114.319 of this title; and
(C)
complies with the standards specified in §114.312
of this title (relating to Low Emission Diesel Standards).
(15)
Motor vehicle - Any self-propelled device powered by a
gasoline fueled spark-ignition engine or a diesel fueled compression-ignition
engine in or by which a person or property is or may be transported, and is
required to be registered under Texas Transportation Code (TTC), §502.002,
excluding vehicles registered under TTC, §502.006(c).
(16)
Motor vehicle fuel - Any gasoline or diesel fuel used
to power gasoline fueled spark-ignition or diesel fueled compression-ignition
engines.
(17)
Non-road equipment - Any device powered by a gasoline
fueled spark-ignition engine or a diesel fueled compression-ignition engine
which is not required to be registered under TTC, §502.002.
(18)
Produce - Perform the process to convert liquid compounds
which are not motor vehicle fuel into motor vehicle fuel, except where a person
supplies motor vehicle fuel to a producer who agrees in writing to further
process the motor vehicle fuel at the production facility and to be treated
as a producer of the motor vehicle fuel, only the final producer shall be
deemed for all purposes under Subchapter H of this chapter to be the producer
of the motor vehicle fuel.
(19)
Producer - Any person who owns, leases, operates, controls,
or supervises a production facility and/or produces motor vehicle fuel.
(20)
Production facility - A facility at which motor vehicle
fuel is produced or that manufactures liquid fuels by distilling petroleum.
(21)
Retail fuel dispensing outlet - Any establishment at which
gasoline and/or diesel fuel is sold or offered for sale for use in motor vehicles,
and the fuel is directly dispensed into the fuel tanks of the motor vehicles
using the fuel.
(22)
Supply - To provide or transfer fuel to a physically separate
facility, vehicle, or transportation system.
This agency hereby certifies that the adoption has been
reviewed by legal counsel and found to be a valid exercise of the agency's
legal authority.
Filed with the Office of
the Secretary of State on December 29, 2000.
TRD-200009080
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Effective date: January 18, 2001
Proposal publication date: August 25, 2000
For further information, please call: (512) 239-0348
2.
LOW EMISSION DIESEL
30 TAC §§114.312 - 114.317, 114.319
STATUTORY AUTHORITY
The amendments are adopted under TWC, §5.103, which authorizes the
commission to adopt rules necessary to carry out its powers and duties under
the TWC; and under the Texas Health and Safety Code, Texas Clean Air Act (TCAA), §382.017,
which authorizes the commission to adopt rules consistent with the policy
and purposes of the TCAA. The amendments are also adopted under TCAA, §382.011,
which authorizes the commission to control the quality of the state's air; §382.012,
which authorizes the commission to prepare and develop a general, comprehensive
plan for the control of the state's air; §382.019, which authorizes the
commission to adopt rules to control and reduce emissions from engines used
to propel land vehicles; §382.037(g), which authorizes the commission
to regulate fuel content if it is demonstrated to be necessary for attainment
of the NAAQS; and §382.039, which authorizes the commission to develop
and implement transportation programs and other measures necessary to demonstrate
attainment and protect the public from exposure to hazardous air contaminants
from motor vehicles.
§114.312.Low Emission Diesel Standards.
(a)
No person shall sell, offer for sale, supply, or offer
for supply, dispense, transfer, allow the transfer, place, store, or hold
any diesel fuel in any stationary tank, reservoir, or other container in the
counties listed in §114.319 of this title (relating to Affected Counties
and Compliance Dates), which may ultimately be used to power a diesel fueled
compression-ignition engine in the affected counties, that does not meet either
the low emission diesel (LED) standards of subsections (b) - (d) of this section,
or the requirements of subsection (f) or (g) of this section.
(b)
Sulfur content.
(1)
The maximum sulfur content of LED shall not exceed 500
parts per million (ppm) by weight per gallon in the counties specified in §114.319(a)
and (b) of this title.
(2)
The maximum sulfur content of LED shall not exceed 15 ppm
by weight per gallon in accordance with the counties and compliance date specified
in §114.319(c) of this title.
(c)
The maximum aromatic hydrocarbon content of LED is 10%
by volume per gallon; or the LED has been reported in accordance with all
of the requirements of §114.313 of this title (relating to Designated
Alternative Limits), where:
(1)
the aromatic hydrocarbon content does not exceed the designated
alternative limit (DAL); and
(2)
the designated alternative limit exceeds 10% by volume,
the excess aromatic hydrocarbon content is fully offset in accordance with §114.313
of this title.
(d)
The minimum cetane number for LED is 48.
(e)
Subsection (a) of this section shall not apply to a sale,
offer for sale, or supply of diesel fuel to a producer where the producer
further processes the diesel fuel at the producer's production facility prior
to any subsequent sale, offer for sale, or supply of the diesel fuel.
(f)
Diesel fuel which has been produced to comply with all
specifications for a Certified Diesel Fuel Formulation as approved by an executive
order by the California Air Resources Board may be used to satisfy the requirements
of subsection (a) of this section.
(g)
Alternative diesel fuel formulations which the producer
has demonstrated to the satisfaction of the executive director and the EPA,
through emissions and performance testing methods prescribed in §114.315(c)
and (d) of this title (relating to Approved Test Methods), as achieving comparable
or better reductions in emissions of oxides of nitrogen, volatile organic
compounds, and particulate matter may be used to satisfy the requirements
of subsections (c) and (d) of this section. For alternative diesel fuel formulations
that incorporate additive systems, the estimated emissions benefits of the
alternative diesel fuel formulation may be determined by comparing the emissions
and performance characteristics of the alternative diesel fuel with the additive
system versus the emissions and performance characteristics of a diesel fuel
without the additive system, as determined by the testing methods prescribed
in §114.315(c) and (d) of this title. The commission recognizes that
fuel content specifications, additive formulation, and testing technology
often include factors that can reasonably be considered proprietary or confidential.
Therefore, proprietary or confidential information supplied by the producer
for evaluation of an alternative diesel fuel formulation must be identified
as such when submitted. Decisions regarding confidentiality will be made subject
to the Texas Public Information Act, Texas Government Code, Chapter 552.
§114.313.Designated Alternate Limits.
(a)
A producer or importer may assign a designated alternative
limit (DAL) for aromatic hydrocarbon content to a final blend of low emission
diesel fuel (LED) produced or imported by the producer or importer, except
for that LED produced in accordance with §114.312(g) of this title (relating
to Low Emission Diesel Standards), if the following conditions are met.
(1)
In no case shall the aromatic hydrocarbon content of the
final blend shown by the sample and test conducted in accordance with §114.315
of this title (relating to Approved Test Methods) exceed the assigned DAL.
(2)
The producer or importer shall notify the executive director
of the volume (in barrels) and the DAL of the final blend. This notification
shall be received by the executive director before the start of physical transfer
of the LED from the production or import facility, and in no case less than
12 hours before the producer either completes physical transfer of the final
blend.
(3)
Within 90 days before or after the start of physical transfer
of any final blend of LED to which a producer or importer has assigned a DAL
exceeding the limit for aromatic hydrocarbon content specified in §114.312(c)
of this title, the producer or importer shall complete physical transfer from
the production or import facility of LED in sufficient quantity and with a
DAL sufficiently below the standard specified in §114.312(c) of this
title to offset the volume of aromatic hydrocarbons in the LED reported in
excess of the standard.
(b)
No person shall sell, offer for sale, or supply LED, in
a final blend to which a producer or importer has assigned a DAL:
(1)
exceeding the standard specified in §114.312(c) of
this title for aromatic hydrocarbon content, where the total volume of the
final blend sold, offered for sale, or supplied exceeds the volume reported
to the executive director in accordance with subsection (a)(2) of this section;
nor
(2)
less than the standard specified in §114.312(c) of
this title for aromatic hydrocarbon content, where the total volume of the
final blend sold, offered for sale, or supplied is less than the volume reported
to the executive director in accordance with subsection (a)(2) of this section.
(c)
Whenever the final blend of a producer or importer includes
volumes of diesel fuel the producer or importer has produced or imported,
and volumes it has not produced or imported, the producer's or importer's
DAL shall apply only to the volume of diesel fuel the producer or importer
has produced or imported. In such a case, the producer or importer shall report
to the executive director in accordance with subsection (a)(2) of this section,
both the volume of diesel fuel produced or imported and the total volume of
the final blend.
§114.315.Approved Test Methods.
(a)
Compliance with the diesel fuel content requirements of §114.312
of this title (relating to Low Emission Diesel Standards) shall be determined
by applying the following test methods and procedures, as appropriate.
(1)
The sulfur content of low emission diesel (LED) shall be
determined by the American Society for Testing and Materials (ASTM) Test Method
D2622-98 (Standard Test Method for Sulfur in Petroleum Products by Wavelength
Dispersive X-ray Fluorescence Spectrometry), dated 1998.
(2)
The aromatic hydrocarbon content of LED shall be determined
by ASTM Test Method D5186-99 (Standard Test Method for Determination of Aromatic
Content and Polynuclear Aromatic Content of Diesel Fuels and Aviation Turbine
Fuels by Supercritical Fluid Chromatography), dated 1999.
(3)
The cetane number of LED shall be determined by ASTM Test
Method D613-95 (Standard Test Method for Cetane Number of Diesel Fuel Oil),
dated 1995.
(4)
The polycyclic aromatic hydrocarbon content of LED shall
be determined by ASTM Test Method D2425-99 (Standard Test Method for Hydrocarbon
Types in Middle Distillates by Mass Spectrometry), dated 1999.
(5)
The nitrogen content of LED shall be determined by ASTM
Test Method D4629-96 (Standard Test Method for Trace Nitrogen in Liquid Petroleum
Hydrocarbons by Syringe/Inlet Oxidative Combustion and Chemiluminescence Detection),
dated 1996.
(6)
The American Petroleum Institute (API) gravity index of
LED shall be determined by ASTM Test Method D287-92 (Standard Test Method
for API Gravity of Crude Petroleum and Petroleum Products (Hydrometer Method)),
dated 1995.
(7)
The viscosity of LED shall be determined by ASTM Test Method
D445-97 (Standard Test Method for Kinematic Viscosity of Transparent and Opaque
Liquids (the Calculation of Dynamic Viscosity)), dated 1997.
(8)
The flashpoint of LED shall be determined by ASTM Test
Method D93-99c (Standard Test Methods for Flash-Point by Pensky-Martens Closed
Cup Tester), dated 1999.
(9)
The distillation temperatures of LED shall be determined
by ASTM Test Method D86-00 (Standard Test Method for Distillation of Petroleum
Products at Atmospheric Pressure), dated 2000.
(b)
Alternatives to the test methods prescribed in subsection
(a) of this section may be used if validated by Title 40 Code of Federal Regulations
(CFR), Part 63, Appendix A (related to Test Methods), Method 301 (related
to Field Validation of Pollutant Measurement Methods from Various Waste Media),
dated December 29, 1992. For the purposes of this subsection, substitute "executive
director" in each location that Test Method 301 references "administrator."
(c)
The executive director, upon application of any producer
or importer, may approve alternative diesel fuel formulations as prescribed
under §114.312(g) of this title in accordance with the following procedures.
(1)
The applicant shall initially submit a proposed test protocol
to the executive director, which shall include:
(A)
the identity of the entity which will conduct the tests
described in paragraph (4) of this subsection;
(B)
test procedures consistent with the requirements of paragraphs
(2) and (4) of this subsection;
(C)
test data showing that the candidate fuel meets the specifications
for Number 1-D or 2-D diesel fuel as specified in ASTM D975-98b (Standard
Specification for Diesel Fuel Oils), dated 1998, and identifying the characteristics
of the candidate fuel identified in paragraph (2) of this subsection;
(D)
test data showing that the fuel to be used as the reference
fuel satisfies the specifications identified in paragraph (3) of this subsection;
(E)
reasonable quality assurance and quality control procedures;
and
(F)
notification of any outlier identification and exclusion
procedure that will be used, and a demonstration that any such procedure meets
generally accepted statistical principles. The tests shall not be conducted
until the protocol is approved by the executive director. Upon completion
of the tests, the applicant may submit an application for certification to
the executive director. The application shall include the approved test protocol,
all of the test data, a copy of the complete test log prepared in accordance
with paragraph (4)(D) of this subsection, a demonstration that the candidate
fuel meets the requirements for certification specified in this subsection,
and other information as the executive director may reasonably require. Upon
review of the certification application, the executive director shall grant
or deny the application. Any denial shall be accompanied by a written statement
of the reasons for denial.
(2)
The applicant shall supply the candidate fuel to be used
in the comparative testing in accordance with paragraph (4) of this subsection.
(A)
The sulfur content, total aromatic hydrocarbon content,
polycyclic aromatic hydrocarbon, nitrogen content, and cetane number of the
candidate fuel shall be determined as the average of three tests conducted
in accordance with the referenced test method specified in subsection (a)
of this section.
(B)
The identity and concentration of each additive in the
candidate fuel shall be determined by a test method specified by the applicant
and approved by the executive director to adequately determine the presence
and concentration of the additive.
(C)
The applicant may also specify any other parameters for
the candidate fuel, along with the test method for determining the parameters.
The applicant shall provide the chemical composition of each additive in the
candidate fuel, except that if the chemical composition of an additive is
not known to either the applicant or to the manufacturer of the additive (if
other), the applicant may provide a full disclosure of the chemical process
of manufacture of the additive in lieu of its chemical composition.
(3)
The reference fuel used in the comparative testing described
in paragraph (4) of this subsection shall be produced from straight-run diesel
fuel by a hydrodearomatization process and shall have the following characteristics
determined in accordance with the referenced test method specified in subsection
(a) of this section:
(A)
sulfur content - as specified in §114.312(b) of this
title;
(B)
total aromatic hydrocarbon content - 10% maximum, volume
percent;
(C)
polycyclic aromatic hydrocarbon content - 1.4%, maximum
weight percent;
(D)
nitrogen content - ten parts per million, maximum;
(E)
cetane number - 48, minimum;
(F)
API gravity index - 33 to 39 degrees;
(G)
viscosity at 40 degrees Celsius - 2.0 to 4.1 centistokes;
(H)
flash point - 130 degrees Fahrenheit, minimum; and
(I)
distillation:
(i)
initial boiling point - 340 to 420 degrees Fahrenheit;
(ii)
10% point - 400 to 490 degrees Fahrenheit;
(iii)
50% point - 470 to 560 degrees Fahrenheit;
(iv)
90% point - 550 to 610 degrees Fahrenheit; and
(v)
end point - 580 to 660 degrees Fahrenheit.
(4)
Exhaust emission tests using the candidate fuel and the
reference fuel specified in paragraph (3) of this subsection shall be conducted
in accordance with the federal test procedures as specified in Title 40 CFR,
Part 86 (Control of Emissions from New and in-Use Highway Vehicles and Engines),
Subpart N (Emission Regulations for New Otto-Cycle and Diesel Heavy-Duty
Engines - Gaseous and Particulate Exhaust Test Procedures), dated 1998.
(A)
The tests shall be performed using a Detroit Diesel Corporation
Series-60 engine or an engine specified by the applicant and approved by the
executive director to be equally representative of the post-1990 model year
heavy-duty diesel engine fleet.
(B)
The comparative testing shall be conducted by a third-party
or third-parties that are mutually agreed upon by the executive director and
the applicant. The applicant shall be responsible for all costs of the comparative
testing.
(C)
The applicant shall conduct a minimum of five exhaust emission
tests on the engine with each fuel, using either of the following sequences,
where "R" is the reference fuel and "C" is the candidate fuel:
(i)
RC, RC, RC, RC, RC (and continuing in the same order);
or
(ii)
RC, CR, RC, CR, RC (and continuing in the same order).
(D)
The applicant shall submit a test schedule to the executive
director at least one week prior to commencement of the tests. The test schedule
shall identify the days on which the tests will be conducted, and shall provide
for conducting the test consecutively without substantial interruptions other
than those resulting from the normal hours of operations at the test facility.
The executive director or his designee shall be permitted to observe any tests.
The party conducting the testing shall maintain a test log which identifies
all tests conducted, all engine mapping procedures, all physical modifications
to or operational tests of the engine, all re-calibrations or other changes
to the test instruments, and all interruptions between tests and the reason
for each such interruption. The party conducting the tests or the applicant
shall notify the executive director by telephone and in writing of any unscheduled
interruption resulting in a test delay of 48 hours or more, and of the reason
for such delay. Prior to restarting the test, the applicant or person conducting
the tests shall provide the executive director with a revised schedule for
the remaining tests. All tests conducted in accordance with the test schedule,
other than any tests rejected in accordance with an outlier identification
and exclusion procedure included in the approved test protocol, shall be included
in the comparison of emissions in accordance with paragraph (5) of this subsection.
(E)
In each test of a fuel, exhaust emissions of oxides of
nitrogen (NO
x
), volatile organic compounds (VOC),
and particulate matter (PM) shall be measured.
(5)
The average emissions during testing with the candidate
fuel shall be compared to the average emissions during testing with the reference
fuel specified in paragraph (3) of this subsection, applying one-sided Student's
t statistics as set forth in Snedecar and Cochran,
Statistical Methods
(7th edition), page 91, Iowa State University
Press, 1980. The executive director shall issue a certification in accordance
with this paragraph only if he or she makes all of the following determinations:
(A)
the average individual emissions of NO
x
, VOC, and PM, respectively, during testing with the candidate fuel
do not exceed the average individual emissions of NO
x
, VOC, and PM, respectively, during testing with the reference fuel;
and
(B)
use of any additive identified in accordance with paragraph
(2)(B) of this subsection in diesel powered engines will not increase emissions
of noxious or toxic substances which would not be emitted by such engines
operating without the additive.
(6)
If the executive director finds that a candidate fuel has
been properly tested in accordance with this subsection, and makes the determinations
specified in paragraph (5) of this subsection, then the executive director
shall issue an approval notification certifying that the alternative diesel
fuel formulation represented by the candidate fuel may be used to satisfy
the requirements of §114.312(a) of this title. The approval notification
shall identify all of the characteristics of the candidate fuel determined
in accordance with paragraph (2) of this subsection.
(A)
The approval notification shall provide that the approved
alternative diesel fuel formulation has the following specifications:
(i)
a sulfur content, total aromatic hydrocarbon content, polycyclic
aromatic hydrocarbon content, and nitrogen content not exceeding that of the
candidate fuel;
(ii)
a cetane number not less than that of the candidate fuel;
and
(iii)
presence of all additives that were contained in the
candidate fuel, in a concentration not less than in the candidate fuel.
(B)
All such characteristics shall be determined in accordance
with the test methods identified in subsection (a) of this section. The approval
notification shall assign an identification number to the specific approved
alternative diesel fuel formulation.
(d)
Notwithstanding subsection (c) of this section, the executive
director, upon application of any producer or importer, may approve alternative
diesel fuel formulations as prescribed under §114.312(g) of this title
which may be used to satisfy the requirements of §114.312(c) and (d)
of this title if the formulations are intended only for use in non-road equipment
and, through emissions and performance testing with supporting data, the producer
or importer has demonstrated to the satisfaction of the executive director
and the EPA as achieving comparable or better reductions in emissions of NO
§114.316.Monitoring, Recordkeeping, and Reporting Requirements.
(a)
Every producer or importer that has elected to sell, offer
for sale, supply, or offer for supply low emission diesel fuel (LED) in counties
listed in §114.319 of this title (relating to Affected Counties and Compliance
Dates) is subject to the requirements of this section. Under these requirements
LED which has been produced or imported must conform with the standards for
sulfur content, aromatic hydrocarbon content, and minimum cetane number as
specified in §114.312 of this title (relating to Low Emission Diesel
Standards) or other standards, including the type and concentration of additive
as specified in accordance with §114.312(g) of this title. All records
relating to LED must contain a statement declaring whether the aromatic hydrocarbon
content of the sample conforms to the basic standard, to a designated alternative
limit (DAL) in accordance with §114.313 of this title (relating to Designated
Alternative Limits), to a limit specified in a Certified Diesel Fuel Formulation
as approved by an executive order issued by the California Air Resources Board
(CARB), or whether the diesel fuel conforms to an alternative diesel fuel
formulation approved under §114.312(g) of this title.
(b)
Each producer or importer of a diesel fuel that conforms
to §114.312(a) - (f) of this title shall sample and test for the sulfur
content, aromatic hydrocarbon content, and minimum cetane number in each final
blend of LED which the producer or importer has produced or imported, by collecting
and analyzing a representative sample of diesel fuel taken from the final
blend, using the methodologies specified in §114.315 of this title (relating
to Approved Test Methods). If a producer or importer blends diesel fuel components
directly to pipelines, tank ships, railway tank cars, or trucks and trailers,
the loading(s) shall be sampled and tested for the sulfur content, aromatic
hydrocarbon content, and minimum cetane number by the producer or importer
or authorized contractor. The producer or importer shall maintain, for two
years from the date of each sampling, records showing the sample date, identity
of blend sampled, container or other vessel sampled, final blend volume, and
the sulfur content, aromatic hydrocarbon content, and minimum cetane number.
All diesel fuel produced by the producer or imported by the importer and not
tested as LED by the producer or importer as required by this section shall
be deemed to exceed the standards specified in §114.312 of this title,
unless the producer or importer demonstrates that the diesel fuel meets those
standards and limits.
(c)
Each producer or importer of a diesel fuel that conforms
to §114.312(g) of this title shall sample and test for the appropriate
components approved by the executive director in each final blend of LED which
the producer or importer has produced or imported, by collecting and analyzing
a representative sample of diesel fuel taken from the final blend, using the
methodologies specified in §114.315 of this title. If a producer or importer
blends diesel fuel components directly to pipelines, tank ships, railway tank
cars, or trucks and trailers, the loading(s) shall be sampled and tested for
the appropriate components approved by the executive director by the producer
or importer or authorized contractor. If the approved blend contains an additive
system, the producer or importer or authorized contractor shall maintain records
showing that sufficient additive was added to maintain the appropriate additive
concentration as approved by the executive director. The producer or importer
shall maintain, for two years from the date of each sampling, records showing
the sample date, identity of blend sampled, container or other vessel sampled,
final blend volume, and the appropriate fuel components. All diesel fuel produced
by the producer or imported by the importer and not tested as LED by the producer
or importer as required by this section shall be deemed to exceed the standards
specified in §114.312 of this title, unless the producer or importer
demonstrates that the diesel fuel meets those standards and limits.
(d)
A producer or importer shall provide to the executive director
any records required to be maintained by the producer or importer in accordance
with this section within five days of a written request from the executive
director, if the request is received before expiration of the period during
which the records are required to be maintained. Whenever a producer or importer
fails to provide records regarding a final blend of LED in accordance with
the requirements of this section, the final blend of diesel fuel shall be
presumed to have been sold by the producer or importer in violation of the
standards specified in §114.312 of this title, to which the producer
or importer has elected to be subject.
(e)
All parties in the distribution chain (producer, importer,
terminals, pipelines, truckers, rail carriers, and retail fuel dispensing
outlets) subject to the provisions of §114.312 of this title must maintain
copies or records of product transfer documents for a minimum of two years
and shall upon request, make such copies or records available to representatives
of the commission, EPA, or local air pollution agency having jurisdiction
in the area. The product transfer documents must contain, at a minimum, the
following information:
(1)
the date of transfer;
(2)
the name and address of the transferor;
(3)
the name and address of the transferee;
(4)
in the case of transferors or transferees who are producers
or importers, the registration number of those persons as assigned by the
commission under §114.314 of this title (relating to Registration of
Diesel Producers and Importers);
(5)
the volume of diesel fuel being transferred;
(6)
the location of the diesel fuel at the time of transfer;
(7)
the following certification statement: "This product complies
with the requirements for low emission diesel fuel specified in Title 30 Texas
Administrative Code, §114.312 and may be used in any Texas county requiring
the use of low emission diesel fuel in compression-ignition engines."; and
(8)
in the case of diesel fuel that was produced under the
requirements of §114.312(f) or (g) of this title, the executive order
number as issued by the CARB or the approval notification number as issued
by the executive director in accordance with §114.315(c)(6) or (d) of
this title.
(f)
For each final blend which is sold or supplied by a producer
or importer from the party's production facility or import facility, and which
contains volumes of diesel fuel that the party has produced and imported and
volumes that the party neither produced nor imported, the producer or importer
shall establish, maintain, and retain adequately organized records containing
the following information.
(1)
The volume of diesel fuel in the final blend that was not
produced or imported by the producer or importer, the identity of the persons(s)
from whom such diesel fuel was acquired, the date(s) on which it was acquired,
and the invoice(s) representing the acquisition(s).
(2)
The sulfur content, aromatic hydrocarbon content, and the
cetane number of the volume of diesel in the final blend that was not produced
or imported by the producer or importer, determined either by:
(A)
sampling and testing by the producer or importer of the
acquired diesel fuel represented in the final blend; or
(B)
written results of sampling and test of the diesel fuel
supplied by the person(s) from whom the diesel fuel was acquired.
(3)
A producer or importer subject to subsection (f) of this
section shall establish such records by the time the final blend triggering
the requirements is sold or supplied from the production or import facility,
and shall retain such records for two years from such date. During the period
of required retention, the producer or importer shall make any of the records
available to the executive director upon request.
(g)
Each producer or importer electing to sell, offer for sale,
supply, or offer to supply LED in accordance with §114.312 of this title
shall provide a report on each final blend and a quarterly summation report
to the executive director no later than the fifteenth of the month following
the end of the calendar quarter. The report on each final blend shall provide,
at a minimum, the information required to be collected by subsections (b),
(c), and (f) of this section. The quarterly report shall provide, at a minimum,
reconciliation of the quarter's transactions relative to the requirements
of subsections (b), (c), and (f) of this section. Updates or revisions to
estimated transaction volumes required by subsections (b) and (c) of this
section shall be included in this report.
(h)
Each producer or importer electing to sell, offer for sale,
supply, or offer to supply LED under §114.312(f) of this title shall
provide to the executive director a copy of the executive order issued by
the CARB for the Certified Diesel Fuel Formulation used to produce the LED
and shall comply with the requirements of subsections (b) and (f) of this
section using the fuel specifications for aromatic hydrocarbon, sulfur, and
cetane set by this executive order.
(i)
Each producer or importer electing to sell, offer for sale,
supply, or offer to supply LED under §114.312(f) of this title shall
sample and test for the polycyclic aromatic hydrocarbon content and nitrogen
content in each final blend of LED which the producer or importer has produced
or imported using the fuel specifications for polycyclic aromatic hydrocarbons
and nitrogen set by the executive order issued by the CARB for the Certified
Diesel Fuel Formulation used to produce the LED, by collecting and analyzing
a representative sample of diesel fuel taken from the final blend using the
methodologies specified in §114.315 of this title and shall include a
record of these tests in the report required by subsection (g) of this section.
§114.317.Exemptions to Low Emission Diesel Requirements.
(a)
Any diesel fuel that is either in a research, development,
or test status; or is sold to petroleum, automobile, engine, or component
manufacturers for research, development, or test purposes; or any diesel fuel
to be used by, or under the control of, petroleum, additive, automobile, engine,
or component manufacturers for research, development, or test purposes, is
exempted from the provisions of this division (relating to Low Emission Diesel),
provided that:
(1)
the diesel fuel is kept segregated from non-exempt product,
and the person possessing the product maintains documentation identifying
the product as research, development, or testing fuel, as applicable, and
stating that it is to be used only for research, development, or testing purposes;
and
(2)
the diesel fuel is not sold, dispensed, or transferred,
or offered for sale, dispensing, or transfer from a retail fuel dispensing
facility. It shall also not be sold, dispensed, or transferred, or offered
for sale, dispensing, or transfer from a wholesale purchaser-consumer facility,
unless such facility is associated with fuel, automotive, or engine research,
development or testing.
(b)
Any diesel fuel that is refined, sold, dispensed, transferred,
or offered for sale, dispensing, or transfer as competition racing fuel is
exempted from the provisions of this division, provided that:
(1)
the fuel is kept segregated from non-exempt fuel, and the
party possessing the fuel for the purposes of refining, selling, dispensing,
transferring, or offering for sale, dispensing, or transfer as competition
racing fuel maintains documentation identifying the product as racing fuel,
restricted for non-highway use in competition racing motor vehicles or engines;
(2)
each pump stand at a regulated facility, from which the
fuel is dispensed, is labeled with the applicable fuel identification and
use restrictions described in paragraph (1) of this subsection; and
(3)
the fuel is not sold, dispensed, transferred, or offered
for sale, dispensing, or transfer for highway use in a motor vehicle.
(c)
The owner or operator of a retail fuel dispensing outlet
is exempt from all requirements of §114.316 of this title (relating to
Monitoring, Recordkeeping, and Reporting Requirements) except §114.316(e)
of this title.
(d)
Diesel fuel that does not meet the requirements of §114.312
of this title (relating to Low Emission Diesel Standards) is not prohibited
from being transferred, placed, stored, and/or held within the affected counties
so long as it is not ultimately used:
(1)
to power a diesel fueled compression-ignition engine in
a motor vehicle in the counties listed in §114.319 of this title, except
for that used in conjunction with purposes stated in subsections (a) and (b)
of this section; or
(2)
to power a diesel fueled compression-ignition engine in
non-road equipment in the counties listed in §114.319(b) of this title,
except for that used in conjunction with purposes stated in subsections (a)
and (b) of this section.
§114.319.Affected Counties and Compliance Dates.
(a)
Beginning May 1, 2002, affected persons in all counties
of Texas shall be in compliance, as applicable, with §§114.312 -
114.317 of this title (relating to Low Emission Diesel Standards; Designated
Alternate Limits; Registration of Diesel Producers and Importers; Approved
Test Methods; Monitoring, Recordkeeping, and Reporting Requirements; and Exemptions
to Low Emission Diesel Requirements) for that diesel fuel which may ultimately
be used to power a diesel fueled compression-ignition engine in a motor vehicle.
(b)
Beginning May 1, 2002, affected persons in the following
counties shall be in compliance with §§114.312 - 114.317 of this
title for that diesel fuel which may ultimately be used to power a diesel
fueled compression-ignition engine in a motor vehicle or in non-road equipment:
(1)
Collin, Dallas, Denton, and Tarrant;
(2)
Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty,
Montgomery, and Waller;
(3)
Hardin, Jefferson, and Orange; and
(4)
Anderson, Angelina, Aransas, Atascosa, Austin, Bastrop,
Bee, Bell, Bexar, Bosque, Bowie, Brazos, Burleson, Caldwell, Calhoun, Camp,
Cass, Cherokee, Colorado, Comal, Cooke, Coryell, De Witt, Delta, Ellis, Falls,
Fannin, Fayette, Franklin, Freestone, Goliad, Gonzales, Grayson, Gregg, Grimes,
Guadalupe, Harrison, Hays, Henderson, Hill, Hood, Hopkins, Houston, Hunt,
Jackson, Jasper, Johnson, Karnes, Kaufman, Lamar, Lavaca, Lee, Leon, Limestone,
Live Oak, Madison, Marion, Matagorda, McLennan, Milam, Morris, Nacogdoches,
Navarro, Newton, Nueces, Panola, Parker, Polk, Rains, Red River, Refugio,
Robertson, Rockwall, Rusk, Sabine, San Jacinto, San Patricio, San Augustine,
Shelby, Smith, Somervell, Titus, Travis, Trinity, Tyler, Upshur, Van Zandt,
Victoria, Walker, Washington, Wharton, Williamson, Wilson, Wise, and Wood.
(c)
Beginning June 1, 2006, affected persons in the counties
listed in subsection (b) of this section shall be in compliance with §114.312(b)(2)
of this title for that diesel fuel which may ultimately be used to power a
diesel fueled compression-ignition engine in a motor vehicle or in non-road
equipment.
This agency hereby certifies that the adoption has been reviewed
by legal counsel and found to be a valid exercise of the agency's legal authority.
Filed
with the Office of the Secretary of State on December 29, 2000.
TRD-200009081
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Effective date: January 18, 2001
Proposal publication date: August 25, 2000
For further information, please call: (512) 239-0348
Subchapter C. VEHICLE INSPECTION AND MAINTENANCE
30 TAC §§114.50-114.53
The Texas Natural Resource Conservation Commission (commission)
adopts amendments to §114.50, Vehicle Emissions Inspection Requirements; §114.51,
Equipment Evaluation Procedures for Vehicle Exhaust Gas Analyzers; §114.52,
Waivers and Extensions for Inspection Requirements; and §114.53, Inspection
and Maintenance Fees. The commission adopts these amendments to Chapter 114
(Control of Air Pollution from Motor Vehicles), and to the state implementation
plan (SIP) in order to control ground-level ozone in the Houston/Galveston
(HGA) ozone nonattainment area. These amendments are one element of the control
strategy for the HGA Post-1999 Rate-of-Progress (ROP)/Attainment Demonstration
SIP. Sections 114.50, 114.52, and 114.53 are adopted
with changes
to the text published in the August 25, 2000, issue of
the
Texas Register
(25 TexReg 8180). Section
114.51 is adopted
without changes
and the
text will not be republished.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE ADOPTED RULES
The HGA ozone nonattainment area is classified as Severe-17 under the Federal
Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401
et seq.), and therefore is required to attain the one-hour ozone standard
of 0.12 parts per million (ppm) by November 15, 2007. In addition, 42 USC, §7502(a)(2),
requires attainment as expeditiously as practicable, and 42 USC, §7511a(d),
requires states to submit ozone attainment demonstration SIPs for severe ozone
nonattainment areas such as HGA. The HGA area, defined by Brazoria, Chambers,
Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has
been working to develop a demonstration of attainment in accordance with 42
USC, §7410. On January 4, 1995, the state submitted the first of its
Post-1996 SIP revisions for HGA.
The January 1995 SIP consisted of urban airshed model (UAM) modeling for
1988 and 1990 base-case episodes, adopted rules to achieve a 9% rate-of-progress
(ROP) reduction in volatile organic compounds (VOC), and a commitment schedule
for the remaining ROP and attainment demonstration elements. At the same time,
but in a separate action, the State of Texas filed for the temporary nitrogen
oxides (NO
x
) waiver allowed by 42 USC, §7511a(f).
The January 1995 SIP and the NO
x
waiver were
based on early base-case episodes which marginally exhibited model performance
in accordance with the United States Environmental Protection Agency (EPA)
modeling performance standards, but which had a limited data set as inputs
to the model. In 1993 and 1994, the commission was engaged in an intensive
data-gathering exercise known as the COAST study. The state believed that
the enhanced emissions inventory, expanded ambient air quality and meteorological
monitoring, and other elements would provide a more robust data set for modeling
and other analysis, which would lead to modeling results that the commission
could use to better understand the nature of the ozone air quality problem
in the HGA area.
Around the same time as the 1995 submittal, EPA policy regarding SIP elements
and timelines went through changes. Two national programs in particular resulted
in changing deadlines and requirements. The first of these programs was the
Ozone Transport Assessment Group. This group grew out of a March 2, 1995 memo
from Mary Nichols, former EPA Assistant Administrator for Air and Radiation,
that allowed states to postpone completion of their attainment demonstrations
until an assessment of the role of transported ozone and precursors had been
completed for the eastern half of the nation, including the eastern portion
of Texas. Texas participated in this study, and it has been concluded that
Texas does not significantly contribute to ozone exceedances in the Northeastern
United States. The other major national initiative that impacted the SIP planning
process is the revision to the national ambient air quality standard (NAAQS)
for ozone. The EPA promulgated a final rule on July 18, 1997 changing the
ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent
with the proposal of the standards, EPA proposed an interim implementation
plan (IIP) that it believed would help areas like HGA transition from the
old to the new standard. In an attempt to avoid a significant delay in planning
activities, Texas began to follow this guidance, and readjusted its modeling
and SIP development timelines accordingly. When the new standard was published,
the EPA decided not to publish the IIP, and instead stated that, for areas
currently exceeding the one-hour ozone standard, that standard would continue
to apply until it is attained. The FCAA requires that HGA attain the standard
by November 15, 2007.
The EPA issued revised draft guidance for areas such as HGA that do not
attain the one-hour ozone standard. The commission adopted on May 6, 1998
and submitted to the EPA on May 19, 1998, a revision to the HGA SIP which
contained the following elements in response to the EPA guidance: UAM modeling
based on emissions projected from a 1993 baseline out to the 2007 attainment
date; an estimate of the level of VOC and NO
x
reductions necessary to achieve the one-hour ozone standard by 2007; a list
of control strategies that the state could implement to attain the one-hour
ozone standard; a schedule for completing the other required elements of the
attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied
a deficiency that the EPA believed made the previous version of that SIP unapprovable;
and evidence that all measures and regulations required by Subpart 2 of Title
I of the FCAA to control ozone and its precursors have been adopted and implemented,
or are on an expeditious schedule to be adopted and implemented.
In November 1998, the SIP revision submitted to the EPA in May 1998 became
complete by operation of law. However, the EPA stated that it could not approve
the SIP until specific control strategies were modeled in the attainment demonstration.
The EPA specified a submittal date of November 15, 1999 for this modeling.
In a letter to the EPA dated January 5, 1999, the state committed to model
two strategies showing attainment.
As the HGA modeling protocol evolved, the state eventually selected and
modeled seven basic modeling scenarios. As part of this process, a group of
HGA stakeholders worked closely with commission staff to identify local control
strategies for the modeling. Some of the scenarios for which the stakeholders
requested evaluation included options such as California-type fuel and vehicle
programs as well as an acceleration simulation mode (ASM-2) equivalent motor
vehicle inspection and maintenance (I/M) program. Other scenarios incorporated
the estimated reductions in emissions that were expected to be achieved throughout
the modeling domain as a result of the implementation of several voluntary
and mandatory state-wide programs adopted or planned independently of the
SIP. It should be made clear that the commission did not propose that any
of these strategies be included in the ultimate control strategy submitted
to the EPA in 2000. The need for and effectiveness of any controls which may
be implemented outside the HGA eight-county area will be evaluated on a county-by-county
basis.
The SIP revision was adopted by the commission on October 27, 1999, submitted
to the EPA by November 15, 1999, and contained the following elements: photochemical
modeling of potential specific control strategies for attainment of the one-hour
ozone standard in the HGA area by the attainment date of November 15, 2007;
an analysis of seven specific modeling scenarios reflecting various combinations
of federal, state, and local controls in HGA (additional scenarios H1 and
H2 build upon Scenario VIf); identification of the level of reductions of
VOC and NO
x
necessary to attain the one-hour
ozone standard by 2007; a 2007 mobile source budget for transportation conformity;
identification of specific source categories which, if controlled, could result
in sufficient VOC and/or NO
x
reductions to attain
the standard; a schedule committing to submit by April 2000 an enforceable
commitment to conduct a mid-course review; and a schedule committing to submit
modeling and adopted rules in support of the attainment demonstration by December
2000.
The April 19, 2000 SIP revision for HGA contained the following enforceable
commitments by the state: to quantify the shortfall of NO
x
reductions needed for attainment; to list and quantify potential
control measures to meet the shortfall of NO
x
reductions needed for attainment; to adopt the majority of the necessary rules
for the HGA attainment demonstration by December 31, 2000, and to adopt the
rest of the shortfall rules as expeditiously as practical, but no later than
July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform
a mid-course review by May 1, 2004; and to perform modeling of mobile source
emissions using the EPA mobile source emissions model (MOBILE6), to revise
the on-road mobile source budget as needed, and to submit the revised budget
within 24 months of the model's release. In addition, if a conformity analysis
is to be performed between 12 months and 24 months after the MOBILE6 release,
the state will revise the motor vehicle emissions budget (MVEB) so that the
conformity analysis and the SIP MVEB are calculated on the same basis.
In order for the state to have an approvable attainment demonstration,
the EPA indicated that the state must adopt those strategies modeled in the
November submittal and then adopt sufficient controls to close the remaining
gap in NO
x
emissions. The modeling and other
analysis supporting these rules and the HGA SIP indicates a gap of approximately
an additional 91 tons per day (tpd) of NO
x
reductions
is necessary for an approveable attainment demonstration. The predicted emission
reductions from these rules are necessary to successfully demonstrate attainment.
The emission reduction requirements included as part of this SIP revision
represent substantial, intensive efforts on the part of stakeholder coalitions
in the HGA area. These coalitions, involving local governmental entities,
elected officials, environmental groups, industry, consultants, and the public,
as well as the commission and the EPA, have worked diligently to identify
and quantify potential control strategy measures for the HGA attainment demonstration.
Local officials from the HGA area formally submitted a resolution to the commission,
requesting the inclusion of many specific emission reduction strategies.
This rule adoption is one element of the control strategy for the HGA SIP.
Adoption and implementation of this control strategy is necessary in order
for the HGA nonattainment area to comply with the requirements of the FCAA
and achieve attainment for ozone. Additional elements of the control strategy
for the HGA SIP are being adopted concurrently in this issue of the
The amount of NO
x
reductions required for
the area to attain the ozone NAAQS has been estimated by extensive use of
sophisticated air quality grid modeling, which because of its scientific and
statutory grounding, is the chief policy tool for designing emission reduction
strategies. The FCAA, 42 USC, §7511a(c)(2), requires the use of photochemical
grid modeling for ozone nonattainment areas designated serious, severe, or
extreme. The modeling has been conducted with input from a technical oversight
committee. Commission staff have continued to improve the air quality modeling
technology and refine emission inventory data. Numerous emission control strategies
were considered in developing the modeling. Varying degrees of reductions
from point sources, on-road and non-road mobile sources, and area sources
were analyzed in multiple iterations of modeling, to test the effectiveness
of different NO
x
reductions. The attainment demonstration
modeling and other analysis submitted for public hearing and comment concurrently
with the HGA SIP show that a significant amount of NO
x
reductions practicably achievable are necessary from ozone control
strategies in order for the HGA nonattainment area to achieve the ozone NAAQS
by 2007, including reductions from surrounding counties included in the HGA
consolidated metropolitan statistical area (CMSA).
Additionally, reductions associated from the ozone control strategies that
will be implemented outside the HGA nonattainment area will benefit the HGA
nonattainment area. This is due to the regional nature of air pollution, the
contribution from mobile sources, and the economies of scale and associated
market advantages related to distribution networks for some strategies. At
the time the 1990 FCAA Amendments were enacted, the focus on controlling ozone
pollution was centered on local controls. However, for many years an ever
increasing number of air quality professionals have concluded that ozone is
a regional problem requiring regional strategies in addition to local control
programs. As nonattainment areas across the United States prepared attainment
demonstration SIPs in response to the 1990 FCAA Amendments, several areas
found that modeling attainment was made much more difficult, if not impossible,
due to high ozone and ozone precursor levels entering from the boundaries
of their respective modeling domains, commonly called transport. Recent science
indicates that regional approaches may provide improved control of ozone air
pollution.
The current SIP revision contains rules, enforceable commitments, photochemical
modeling analyses, and calculation of the remaining NO
x
reductions required to reach attainment (gap calculation) in support
of the HGA ozone attainment demonstration. In addition, this SIP contains
post-1999 ROP plans for the milestone years 2002 and 2005, and for the attainment
year 2007. The SIP also contains enforceable commitments to implement further
measures, if needed, in support of the HGA attainment demonstration, as well
as a commitment to perform and submit a mid-course review.
The HGA ozone nonattainment area will need to ultimately reduce NO
The commission is proposing an air control strategy for NO
x
reductions which requires emissions testing of motor vehicles that
are registered and primarily operated in the HGA ozone nonattainment area.
The testing would use ASM-2 and on-board diagnostic (OBD) technologies. This
adopted I/M program was modeled to cover the eight-county region comprising
the HGA nonattainment area. The adopted I/M program will reduce NO
x
emissions from on-road vehicles in the HGA ozone nonattainment area
by 36.20 tpd.
The adopted revisions will modify the vehicle emissions testing program
by implementing ASM-2 testing in the HGA ozone nonattainment area. Unlike
the current two-speed idle (TSI) test, ASM-2 technology has the ability to
detect NO
x
emissions. Because NO
x
is a precursor to ground-level ozone formation, reduced NO
x
and VOC emissions will result in ground-level ozone reduction.
The amendments addressed in these rule changes include: changing the testing
technology in the HGA area to ASM-2 and OBD for Harris County beginning May
1, 2002; implementing ASM-2 and OBD in Brazoria, Fort Bend, Galveston, and
Montgomery Counties beginning May 1, 2003; implementing ASM-2 and OBD in Chambers,
Liberty, and Waller Counties beginning May 1, 2004, and increasing the emissions
inspection fee. The commission is adopting a phased approach to make for a
smoother implementation of the adopted I/M program, while still providing
significant air quality improvements. In addition, the adopted rules incorporate
changes to the exhaust analyzer technical specifications which will apply
in every I/M program area.
The commission solicited comments on the option of Chambers, Liberty, and
Waller Counties individually or collectively developing alternative air control
strategies, other than an I/M program, to meet or exceed the NO
x
emission reductions that are anticipated from the adopted I/M program.
The initial estimated I/M NO
x
emission reductions
for Chambers County were .98 tpd, for Liberty County were .94 tpd, and for
Waller County were .77 tpd, for a combined estimated NO
x
emissions reduction of 2.69 tpd. The commission considered alternatives
during the comment period and made a final determination. However, the remote
sensing component implemented in Harris County will continue to cover vehicles
registered in these counties even if an alternative control strategy is accepted
by the commission.
The commission received thirteen comments to omit Chambers, Liberty, and
Waller Counties. All comments are addressed in the ANALYSIS OF TESTIMONY section
of this preamble.
In its effort to ensure that the SIP strategies impose no more burden than
necessary to protect health and welfare, the commission decided to provide
Chambers, Liberty, and Waller Counties, and their respective largest municipality,
the flexibility to submit by May 1, 2002, individually or collectively, a
resolution that is approved by the commission and the EPA as an alternative
air control strategy. The resolution should provide a control strategy that
will provide modeled reductions of VOC and NO
x
equivalent to the reductions that have been modeled for these counties through
the implementation of the I/M program. The estimated "COAST Update October
2000" NO
x
emission reductions are: Chambers County,
1.25 tpd; Liberty County, 1.06 tpd; and Waller County, .75 tpd, for a combined
estimated NO
x
emissions reduction of 3.06 tpd.
If emission reductions from the alternative plan are in whole or part from
stationary sources, appropriate ratios must be used to reflect the different
impact which mobile sources have on air quality.
Based on the EPA notice of proposed rulemaking (NPRM) dated September 20,
2000, "Amendments to Vehicle Inspection Maintenance Program Equipment Requirements
Incorporating the Onboard Diagnostic Check," the commission amended the I/M
rules to allow OBD testing in lieu of tailpipe testing, for model year vehicles
1996 and newer, beginning May 1, 2002.
The commission solicited comment on additional flexibility relating to
rule content and implementation which have not been addressed in this or other
concurrent rulemakings. The flexibility may be available for both mobile and
stationary sources. Additional flexibility may also be achieved through innovative
and/or emerging technology which may become available in the future. Additional
funding sources for incentive programs may become available to substitute
for some of the measures considered here. The commission received no comments
on additional flexibility relating to rule content and implementation.
SECTION BY SECTION DISCUSSION
Adopted amendments to §114.50 establish revised program requirements
for the state I/M program. The adopted program amendments concern the applicability
and control requirements. The result of these amendments is to incorporate
the entire HGA nonattainment area into the full I/M program in a phased manner.
Section 114.50(a)(1) has been amended to extend TSI testing until April 30,
2002, to allow flexibility in acquiring new test equipment for the program.
This is a change from the proposed rules based upon the EPA NPRM. Section
114.50(a)(2)(A) has been amended to provide for a May 1, 2002 start date for
OBD testing in Dallas/Fort Worth (DFW) program area. Also, a new requirement
has been added to ensure all vehicles that cannot be OBD tested will receive
an EPA-approved tailpipe test. Section 114.50(a)(2)(B) and (C) have been deleted
and Subparagraph (D) has been renumbered (B). Section 114.50(a)(3) has been
amended by adding vehicles which are "registered and primarily operated in
the extended DFW (EDFW), area" and subsection (a)(3)(A) was amended to reflect
that vehicles which cannot be OBD tested will receive an EPA-approved tailpipe
test. Requirements proposed in §114.50(a)(2) and (3) for all testing
stations to offer both an OBD and ASM-2 test have been deleted. Adopted §114.50(a)(4)
is amended by deleting "Harris County of" the HGA program area. Section 114.50(a)(4)(A)
has been amended to provide for a start date of May 1, 2002, for OBD testing
in Harris County. Also, a new requirement has been added to ensure all vehicles
registered and primarily operated in Harris County that cannot be OBD tested
will receive an EPA-approved tailpipe test. The requirement in this section
that the OBD test be conducted in conjunction with the TSI test has been deleted.
Subparagraph (B) and proposed new subparagraph (C) have been deleted. New
subparagraph (D) has been renumbered (B) and the requirement for emissions
test stations to offer both an OBD test and ASM-2 test has been deleted. New
subparagraph (E) has been renumbered (C) and the requirement of an ASM-2 test
being conducted in conjunction with an OBD test was deleted. Subparagraph
(F) has been renumbered (D) and the requirement for emissions test stations
to offer both an OBD test and ASM-2 test has been deleted. New subparagraph
(G) has been renumbered (E) and the requirement of an ASM-2 test being conducted
in conjunction with an OBD test deleted. New subparagraph (H) has been renumbered
(F) and the requirement of emissions test stations to offer both an OBD test
and ASM-2 test has been deleted. New subparagraph (G) allows Chambers, Liberty,
and Waller Counties, and their respective largest municipality to submit by
May 1, 2002, individually or collectively, resolutions to implement an alternative
control strategy. Should these strategies provide equivalent modeling credits
that each of the counties would have received for the I/M program, and they
are approved by the commission and the EPA, then subparagraphs (E) and (F)
shall not apply. Subsection (a)(5)(A) has been amended to provide for a start
date of May 1, 2002, for OBD testing in the El Paso program area. Also, a
new requirement has been added to ensure all vehicles that cannot be OBD tested
will receive an EPA-approved tailpipe test. Subparagraph (B) has been amended
to provide for a start date of May 1, 2002, and the requirement that emissions
test stations must offer both TSI and OBD test has been deleted.
Section 114.50(b)(3) is amended by adding "HGA" after EDFW to the program
areas and deleting "or Harris County" concerning vehicle recall notification.
Section 114.51 is amended to update the equipment evaluation procedures
for vehicle emissions test equipment. This section currently specifies application,
certification, maintenance, and service requirements for manufacturers or
distributors of vehicle emissions testing equipment seeking approval of an
exhaust gas analyzer or analyzer system for use in the Texas I/M program.
Section 114.51(a) currently specifies a date of March 15, 2000, for the exhaust
analyzer technical specifications known as "Specifications for Preconditioned
Two Speed Idle Vehicle Exhaust Gas Analyzer Systems for use in the Texas Vehicle
Emissions Testing Program." In order to incorporate new and updated specifications
into the program, the adopted rule amendments specify a date of November 1,
2000, for both the TSI exhaust analyzer technical specifications, and the
"Specifications for Acceleration Simulation Mode Vehicle Exhaust Gas Analyzer
System for use in the Texas Vehicle Emissions Testing Program."
Proposed amendments to §114.52 would have established the schedule
for when motorists in specific counties become eligible for waivers and extensions.
The schedule was consistent with the dates for the implementation of the annual
emissions testing program in each county. However, the proposed language implied
that motorists who fail an on-road test would not be able to apply for a waiver.
The commission determined that the proposed revision was not needed and therefore
removed the proposed language on adoption.
Adopted amendments to §114.53 establish fee schedules for the different
counties which must be paid for the vehicle emissions inspection at an inspection
station. Section 114.53(a)(1) has changed to reflect TSI testing will be performed
through April 30, 2002, in Dallas, Tarrant, Harris, and El Paso program areas.
Inspection stations conducting TSI testing through April 30, 2002, shall collect
a test fee of $13 and shall remit $1.75 to the Texas Department of Public
Safety (DPS). Paragraphs (2) - (5), relating to I/M inspections fees, have
been deleted and replaced with language that clarifies emissions inspection
test fees. The new language organizes test fees and start dates by program
areas making it clear and concise. New paragraph (2) is being adopted to provide
for the collection of fees by those inspection stations in El Paso County
conducting TSI testing or OBD checks beginning May 1, 2002. Emission inspection
stations under paragraph (2) shall collect a test fee of $14. New paragraph
(3) explains that in the DFW program area beginning May 1, 2002, and in the
EDFW program area beginning May 1, 2003, any emissions inspection station
conducting an ASM-2 or OBD emissions test shall collect a test fee of $22.50.
New paragraph (4) explains that in the HGA program area in Harris County beginning
May 1, 2002, and beginning May 1, 2003 in Brazoria, Fort Bend, Galveston,
and Montgomery Counties, and beginning May 1, 2004, in Chambers, Liberty,
and Waller Counties any emissions inspection station conducting an ASM-2 or
OBD emissions test shall collect a test fee of $22.50. The commission is still
considering how much of the test fee should go to the state and will propose
future rulemaking to clarify that amount.
In addition to the adopted amendments, the adopted revisions to the SIP
narrative clarify the new program elements such as applicability changes;
new performance standards; emissions testing network type; emissions testing;
affected vehicle populations; enforcement actions related to vehicles and
service providers; on-road vehicle emissions testing; and the implementation
schedule.
FINAL REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the rulemaking action in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225, and has determined
that the rulemaking does not meet the definition of a "major environmental
rule" as defined in that statute. "Major environmental rule" means a rule,
the specific intent of which is to protect the environment or reduce risks
to human health from environmental exposure and that may adversely affect
in a material way the economy, a sector of the economy, productivity, competition,
jobs, the environment, or the public health and safety of the state or a sector
of the state.
These adopted rules do not meet any of the four applicability criteria
for requiring a regulatory analysis of "major environmental rule" as defined
in the Texas Government Code. Section 2001.0225 applies only to a major environmental
rule the result of which is to: 1) exceed a standard set by federal law, unless
the rule is specifically required by state law; 2) exceed an express requirement
of state law, unless the rule is specifically required by federal law; 3)
exceed a requirement of a delegation agreement or contract between the state
and an agency or representative of the federal government to implement a state
and federal program; or 4) adopt a rule solely under the general powers of
the agency instead of under a specific state law.
As discussed earlier in this preamble, this rule adoption is one element
of the control strategy for the HGA SIP. Adoption and implementation of this
control strategy is necessary in order for the HGA nonattainment area to comply
with the requirements of the FCAA and achieve attainment for ozone. Additional
elements of the control strategy for the HGA SIP are being adopted concurrently
in this issue of the
Texas Register,
or were
included in the HGA SIP considered by the commission on December 6, 2000,
and planned to be submitted to EPA by December 31, 2000.
The adopted amendments to Chapter 114 are intended to protect the environment
or reduce risks to human health from environmental exposure to ozone. However,
the inspection stations in and around nonattainment areas would not normally
be considered a sector of the economy. In addition, the commission structured
the fees in this program to ensure that most additional equipment costs can
be recovered. Therefore, the adopted rules do not affect in a material way,
the economy, a sector of the economy, productivity, competition, jobs, the
environment, or the public health and safety of the state or a sector of the
state. The adopted amendments are intended to establish a vehicle emissions
testing program as part of the control strategy to reduce NO
x
emissions necessary for the counties included in the HGA nonattainment
area to be able to demonstrate attainment with the ozone NAAQS. The adopted
amendments are one element of the HGA Post-1999 Rate-of-Progress/Attainment
Demonstration SIP. As defined in Texas Government Code, §2001.0225 only
applies to a major environmental rule, the result of which is to: exceed a
standard set by federal law, unless the rule is specifically required by state
law; exceed an express requirement of state law, unless the rule is specifically
required by federal law; exceed a requirement of a delegation agreement or
contract between the state and an agency or representative of the federal
government to implement a state and federal program, or; adopt a rule solely
under the general powers of the agency instead of under a specific state law.
This rulemaking does not meet any of these four applicability requirements
of a "major environmental rule."
These rules do not exceed an express standard set by federal law, since
they implement requirements of the FCAA. Specifically, the emission testing
program within this proposal was developed in order to meet the ozone NAAQS
set by the EPA under 42 USC, §7409, and therefore meets a federal requirement.
Provisions of 42 USC, §7410, require states to adopt a SIP which provides
for "implementation, maintenance, and enforcement" of the primary NAAQS in
each air quality control region of the state. These rules were specifically
developed as part of an overall control strategy to meet the ozone NAAQS set
by the EPA under 42 USC, §7409. Both a plan and emission reductions are
required to assure that the nonattainment areas of the state will be able
to meet the attainment deadlines set by the FCAA. The EPA has provided the
criteria for both the submission and evaluation of attainment demonstrations
developed by states to comply with the FCAA. This criteria requires states
to provide, in addition to other information, photochemical modeling, and
an analysis of specific emission reduction strategies necessary to attain
the NAAQS. The commission's photochemical modeling and other analysis indicate
that substantial emission reductions from both mobile and point source categories
are necessary in order to demonstrate attainment. In this case, this rulemaking
is intended to achieve reductions in ozone precursor emissions in the HGA
nonattainment area. Additionally, nonattainment areas which are classified
as severe are specifically required to include enhanced inspection and maintenance
programs as part of their SIP under 42 USC, §7511a. These rules are adopted
to meet that provision. Specifically, as noted elsewhere in this rule preamble,
the emission reductions associated with these rules are a necessary element
of the attainment demonstration required by the FCAA.
In addition, 42 USC, §7502(a)(2), requires attainment as expeditiously
as practicable, and 42 USC, §7511a(d), requires states to submit ozone
attainment demonstration SIPs for severe ozone nonattainment areas such as
HGA. By policy, the EPA requires photochemical grid modeling to demonstrate
whether the 42 USC, §7511a(f), NO
x
measures
would contribute to ozone attainment. The commission has performed photochemical
grid modeling which predicts that NO
x
emission
reductions, such as those required by these rules, will result in reductions
in ozone formation in the HGA ozone nonattainment area and help bring HGA
into compliance with the air quality standards established under federal law
as NAAQS for ozone. The 42 USC, §7511a(f), exemption from NO
x
measures for HGA expired on December 31, 1997. The expiration of
the exemption under 42 USC, §7511a(f), was based on the finding that
NO
x
reductions in HGA are necessary for attainment
of the ozone standard. Therefore, the adopted amendments are necessary components
of and consistent with the ozone attainment demonstration SIP for HGA, required
by 42 USC, §7410.
During the 75th Legislative Session, Senate Bill (SB) 633 amended the Texas
Government Code to require agencies to perform a regulatory impact analysis
(RIA) of certain rules. The intent of SB 633 was to require agencies to conduct
an RIA of extraordinary rules. With the understanding that this requirement
would seldom apply, the commission provided a cost estimate for SB 633 that
concluded "based on an assessment of rules adopted by the agency in the past,
it is not anticipated that the bill will have significant fiscal implications
for the agency due to its limited application." The commission also noted
that the number of rules that would require assessment under the provisions
of the bill was not large. This conclusion was based, in part, on the criteria
set forth in the bill that exempted proposed rules from the full analysis
unless the rule was a major environmental rule that exceeds a federal law.
As previously discussed, 42 USC does not require specific programs, methods,
or reductions in order to meet the NAAQS; thus, states must develop programs
for each nonattainment area to ensure that area will meet the attainment deadlines.
Because of the ongoing need to address nonattainment issues, the commission
routinely proposes and adopts SIP rules. The legislature is presumed to understand
this federal scheme. If each rule proposed for inclusion in the SIP was considered
to be a major environmental rule that exceeds federal law, then every SIP
rule would require the full RIA contemplated by SB 633. This conclusion is
inconsistent with the conclusions reached by the commission in its cost estimate
and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature
is presumed to understand the fiscal impacts of the bills it passes, and that
presumption is based on information provided by state agencies and the LBB,
the commission believes that the intent of SB 633 was only to require the
full RIA for rules that are extraordinary in nature. While the SIP rules will
have a broad impact, that impact is no greater than is necessary or appropriate
to meet the requirements of the FCAA.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
It is presumed that "when an agency interpretation is in effect at the time
the legislature amends the laws without making substantial change in the statute,
the legislature is deemed to have accepted the agency's interpretation."
The commission's interpretation of the RIA requirements is also supported
by a change made to the Texas Administrative Procedure Act by the legislature
in 1999. In an attempt to limit the number of rule challenges based upon APA
requirements, the legislature clarified that state agencies are required to
meet these sections of the APA against the standard of "substantial compliance."
Texas Government Code, §2001.035. The legislature specifically identified
Texas Government Code, §2001.0225 as falling under this standard. The
commission has substantially complied with the requirements of §2001.0225.
Therefore, in addition to not exceeding an express standard set by federal
law, these rules do not exceed state requirements, and are not adopted solely
under the general powers of the agency because the provisions of the TCAA, §§382.011,
382.012, 382.017, 382.019, 382.037 - 382.038, and 382.039 authorize the commission
to implement a plan for the control of the states air quality, including measures
necessary to meet federal requirements. The remaining applicability criteria,
pertaining to exceeding a delegation agreement or contract between the state
and the federal government does not apply. Thus, the commission is not required
to conduct a regulatory analysis as provided in Texas Government Code, §2001.0225.
Comments received during the comment period regarding the draft RIA are
addressed in the ANALYSIS OF TESTIMONY section of this preamble.
TAKINGS IMPACT ASSESSMENT
The commission evaluated this rulemaking action and performed an analysis
of whether the rules are subject to Texas Government Code, Chapter 2007. The
following is a summary of that analysis. The specific purpose of the rulemaking
action is to implement a revised I/M program in the HGA ozone nonattainment
area as part of the strategy to reduce emissions of ozone precursors necessary
for the area to be able to demonstrate attainment with the ozone NAAQS.
Promulgation and enforcement of the rules will not burden private, real
property because this rulemaking action does not require the installation
of permanent equipment. Also, Texas Government Code, §2007.003(b)(13),
states that Chapter 2007 does not apply to an action that: 1) is taken in
response to a real and substantial threat to public health and safety; 2)
is designed to significantly advance the health and safety purpose; and 3)
does not impose a greater burden than is necessary to achieve the health and
safety purpose. Although the rule amendments do not directly prevent a nuisance
or prevent an immediate threat to life or property, they do prevent a real
and substantial threat to public health and safety and significantly advance
the health and safety purpose. In addition, §2007.003(b)(4) provides
that Chapter 2007 does not apply to these adopted rules since they are reasonably
taken to fulfill an obligation mandated by federal law. The amendments will
implement requirements of 42 USC, §7410. This action is taken in response
to the HGA area exceeding the NAAQS for ground-level ozone, which adversely
affects public health, primarily through irritation of the lungs. The action
significantly advances the health and safety purpose by reducing ambient NO
The commission has included elsewhere in this preamble its reasoned justification
for adopting this strategy and has explained why it is a necessary component
of the SIP, which is federally mandated. This discussion, as well as the HGA
SIP which is being adopted concurrently, explains in detail that every rule
in the HGA SIP package is necessary and that none of the reductions in those
packages represent more than is necessary to bring the area into attainment
with the NAAQS. For these reasons the rules do not constitute a takings under
Chapter 2007 and does not require additional analysis. Comments received during
the comment period regarding the takings impact assessment (TIA) are addressed
in the ANALYSIS OF TESTIMONY section of this preamble.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that this rulemaking action relates to an action
or actions subject to the Texas Coastal Management Program (CMP) in accordance
with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources
Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter
281, Subchapter B, Consistency with the CMP. As required by 31 TAC §505.11(b)(2)
and 30 TAC §281.45(a)(3) relating to actions and rules subject to the
CMP, commission rules governing air pollutant emissions must be consistent
with the applicable goals and policies of the CMP. The commission reviewed
this rulemaking action for consistency with the CMP goals and policies in
accordance with the rules of the Coastal Coordination Council, and determined
that the action is consistent with the applicable CMP goals and policies.
The CMP goal applicable to this rulemaking action is the goal to protect,
preserve, and enhance the diversity, quality, quantity, functions, and values
of coastal natural resource areas (31 TAC §501.12(l)). No new air contaminants
will be authorized and NO
x
air emissions will
be reduced as a result of these rule amendments. The CMP policy applicable
to this rulemaking action is the policy (31 TAC §501.14(q)) that commission
rules comply with federal regulations in 40 Code of Federal Regulations (CFR)
to protect and enhance air quality in the coastal area (31 TAC §501.14(q)).
This rulemaking action will have a beneficial effect on SIP emissions reduction
obligations relating to reasonable further progress and attainment demonstrations
by making additional emissions reductions over those made by the existing
I/M program. Therefore, in compliance with 31 TAC §505.22(e), this rulemaking
is consistent with CMP goals and policies.
The commission solicited comments on the consistency of the proposed rules
with the CMP during the public comment period and received no comments.
HEARINGS AND COMMENTERS
The commission held public hearings on this proposal at the following locations:
September 18, 2000, in Conroe and Lake Jackson; September 19, 2000 in Houston
(two hearings); September 20, 2000, in Katy and Pasadena; September 21, 2000,
in Beaumont, Amarillo, and Texas City; September 22, 2000, in Dayton, El Paso,
and Arlington; and September 25, 2000, in Austin and Corpus Christi. The comment
period closed at 5:00 p.m. on September 25, 2000.
Forty-six persons provided oral testimony at the hearings and 167 persons
submitted written testimony. The following provided both oral and/or submitted
written testimony: Alliance of Automobile Manufacturers (Alliance); Association
of International Automobile Manufacturers (AIAM); Baker Botts (Baker Botts);
Brazoria County Judge John Willy (Brazoria County); Brazoria County Commissioners
Court through Brazoria County Criminal District Attorney's Office (Brazoria
CCC); Business Coalition for Clean Air (BCCA); Chambers County Judge Jimmy
Sylvia (Chambers County); City of Houston (Houston); City of Missouri City
(Missouri City); Environmental Systems Products (ESP); ExxonMobil Corporation
(ExxonMobil); Grandparents of East Harris County (GEHC); Harris County Judge
Robert Eckels (Harris County); Houston-Galveston Area Council (HGAC); JB Services
(JBS); Liberty County Judge Lloyd Kirkhall (Liberty County); Liberty County
Sheriff Gregg Arthur (Liberty County Sheriff); Montgomery County Judge Allen
Sadler (Judge Sadler); Mothers for Clean Air (MCA); National Motorists Association
(NMA); Phillips 66 Company (Phillips 66); Regional Air Quality Consensus Group
(RAQCG); HGAC on behalf of the RAQCG (RAQCG); Sierra Club, Houston Regional
Group (Sierra-Houston); Jan Horn on behalf of State Representative Jerry Madden
Representative Madden); State Representative Zeb Zbranek (Representative Zbranek);
Laura Silagy on behalf of State Senator David Bernsen (Senator Bernsen), SPX
Corporation (SPX); Texas Association of Business and Chambers of Commerce
(TABCC); Texas Automotive Dealers Association (TADA); Texas Chemical Council
(TCC); the League of Women Voters of Texas (LWV-TX); EPA, and 186 individuals.
The following commenters generally supported the proposal: Alliance, Baker
Botts, BCCA, Houston, ESP, ExxonMobil, GEHC, Harris County, JBS, HGAC, MCA,
Phillips 66, RAQCG, Representative Madden, SPX, TABCC, TCC, LWV-TX, the EPA,
and 34 individuals.
The following commenters generally opposed the proposal: Brazoria County,
Chambers County, Missouri City, Liberty County, Montgomery County, NMA, Sierra-Houston,
Liberty County Sheriff, TADA, and 40 individuals.
The following commenters suggested changes to the proposal as stated in
the ANALYSIS OF TESTIMONY section of this preamble: Alliance, AIMA, Chambers
County, ESP, Houston, Harris County, HGAC, Sierra-Houston, Liberty County,
LWV-TX, MCA, Judge Sadler, RAQCG, Representative Zbranek, Senator Bernsen,
SPX, TADA, and 39 individuals.
ANALYSIS OF TESTIMONY
Emissions Testing Fees
Three individuals did not want the test fee increased. In addition, 17
individuals expressed concern that raising the test fee will place a burden
on the elderly, young people, and those who are the least able to afford the
probable additional cost of car repair, or replacement.
The fee increase is necessary to cover the cost of purchasing new vehicle
emissions test equipment and associated costs to include, but not limited
to, labor, training, warranties, insurance, and consumable items (such as
calibration gases) used in conducting emissions tests. However, vehicles that
are properly maintained should have no problem passing the emissions test
regardless of their age. In the event that repairs are necessary, the commission
acknowledges that these vehicle repairs may be costly, but there are mechanisms
in place (waivers and extensions) that help alleviate the cost of emissions
repairs for those who need help. The vehicle emissions testing program includes
two waiver options: the minimum expenditure waiver, and the individual vehicle
waiver. The minimum expenditure waiver is available to those who have made
repairs to their vehicle within the established criteria and met the dollar
limits established by the EPA rule. The individual vehicle waiver is for those
who cannot meet emissions standards despite every reasonable effort by the
motorist. In addition to these two waivers, the low-income time extension
is available for those who can demonstrate a financial inability to either
afford adequate repairs or meet the applicable minimum expenditure waiver
amount. The waivers and time extension are a way to ensure that motorists
who are making a "good faith" effort to comply with the I/M program requirements
do not incur excessive repair costs and are not excessively inconvenienced.
The commission made no changes to the rule in response to this comment.
Vehicle Coverage
A classic car collector wanted to know what the requirements will be for
his 1974, 1975, and 1977 cars in Brazoria County starting in 2003.
Section 114.50(a) excludes antique vehicles registered with the Texas Department
of Transportation (TxDOT) from emissions testing. Additionally, the program
is designed with a "rolling" 24-year window with the most recent 24 model
years being subject to the I/M program. The "rolling" 24-year window option
was selected due to the small amount of vehicles that are on the road after
25 years and the large percentage of those on the road being classified as
classics and/or antiques, which are not subject to emissions testing. In 2003,
emissions testing is required only on vehicles 2 - 24 years of age, because
none of the stated vehicles will be required to undergo emissions testing.
Four individuals wanted tailpipe testing for all vehicles, including gasoline-powered
trucks and sport utility vehicles (SUV).
The I/M program tests all model year 2 - 24 years gasoline-powered vehicles,
including trucks and SUVs. This allows a two-year exemption for the newest
vehicles which are less likely to fail an emissions test. Vehicles that are
25 years and older are exempt for several reasons: many older vehicles were
not required to have many of the pollution control devices now required; a
large percentage of vehicles in this age group are classified as classics
or antiques; and the vehicles in this age group make up a small percentage
(approximately 2.5%) of the total fleet and drive fewer miles per year making
their overall emissions impact relatively small. The commission made no changes
to the rule in response to this comment.
The RAQCG and the HGAC supported the proposed I/M program, but recommended
that the commission should consider a fee for exempting newer model year vehicles
from testing, and the proceeds of such fees to be used for purchasing or removing
high-emitting vehicles from the region's fleet or other emissions reduction
programs.
As the requirement to test vehicles 2 - 24 years old is established by
the state legislature (SB 1856 of the 75th Legislature), the commission does
not have the authority to exempt some of these model years from the program.
The commission made no changes to the rules in response to these comments.
Two individuals recommended exempting vehicles under five years of age.
In addition, it was also recommended that vehicles over 25 years old should
be exempt and should pay a fee that could be used to fund other NO
x
reduction projects.
The requirement to test vehicles 2 - 24 years old is set by state statute
(SB 1856 of the 75th Legislature). These vehicles account for the vast majority
of vehicles on the road and the vehicle miles traveled, which have a direct
correlation to the impact on air quality. The failure rate for vehicles less
than five years old is approximately 1%. Because some newer models do fail
the test and because vehicles subject to the testing are more likely to be
properly maintained, the amount of emissions reductions benefits that can
be claimed for an I/M program is reduced as more model years are exempted
from the program. In addition, since many of the vehicles under five years
old are still under the manufacturer's warranty, identifying emissions-related
problems could be viewed as consumer protection and potentially may save the
vehicle's owner future repair costs.
Vehicles that are 25 years and older are exempt for several reasons: many
older vehicles were not required to have many of the pollution control devices
now required; a large percentage of vehicles in this age group are classified
as classics or antiques; and the vehicles in this age group make up a small
percentage (approximately 2.5%) of the total fleet and drive fewer miles per
year making their overall emissions impact relatively small.
It is beyond the scope of this rulemaking to charge a fee to owners of
vehicles already exempt from the program. The commission made no changes to
the rules in response to these comments.
One individual felt that vehicles with rotary powered engines should be
exempt from emissions testing since a rotary engine does not produce NO
According to the National Center for Vehicle Emissions Control and Safety
at Colorado State University, all gasoline-powered vehicles produce hydrocarbons
(HC), carbon monoxide (CO), and NO
x
emissions.
This includes rotary engine vehicles. Therefore, these vehicles will not be
exempt from emissions testing. If the use of an aftermarket part causes the
vehicle tailpipe emissions to be adversely affected, then the modification
is considered to be tampering. The EPA anti-tampering enforcement policy states
that the EPA will not consider any modification to a certified configuration
to be a violation of federal law if there is a reasonable basis that emissions
are not adversely affected. Vehicles that have been modified from their original
certified configuration will not be exempt from tailpipe testing. The purpose
of the testing, which is to ensure that the emissions control system is working
properly, is still a valid purpose for modified vehicles. The commission made
no changes to the rules in response to these comments.
One individual wanted vehicles over 24 years old tested.
The requirement to test vehicles is set by state statute (SB 1856 of the
75th Legislature). Vehicles that are 25 years and older are exempt for several
reasons: many older vehicles were not required to have many of the pollution
control devices now required; a large percentage of vehicles in this age group
are classified as classics or antiques; and the vehicles in this age group
make up a small percentage (approximately 2.5%) of the total fleet and drive
fewer miles per year making their overall emissions impact relatively small.
The commission made no changes to the rules in response to this comment.
One individual recommended I/M inspections must cover all mobile vehicles
(cars to heavy diesel) under conditions realistically simulating in-use operating
conditions by mid-year 2002, as well as including tests for catalyst integrity.
The commission is adopting a phased approach to make for a smooth implementation
while still providing significant air quality improvements. All gasoline-powered
motor vehicles 2 - 24 years old are subject to an annual emissions inspection.
Military tactical vehicles, motorcycles, diesel-powered vehicles, dual-fueled
vehicles which cannot operate using gasoline, and antique vehicles registered
with the TxDOT are excluded from the program. While the commission is currently
researching the feasibility of heavy-duty diesel vehicle testing, diesel testing
is outside the scope of this rulemaking. The catalytic converter is a major
emission control component for the control of NO
x
.
The ASM-2 test will identify vehicles with excessive NO
x
emissions which is usually caused by a malfunctioning catalytic converter
or exhaust gas recirculation (EGR) valve. The ASM-2 test, which is required
in the HGA nonattainment area, closely simulates in-use operating conditions
by using a dynamometer. The commission made no changes to the rules in response
to these comments.
One individual recommended all vehicles that are used inside private plants
should be required to pass an emissions test.
According to the Texas Transportation Code (TTC), §502.002, the vehicle
emissions testing program affects vehicles registered with TxDOT to be driven
on public roads. Since the plant's roads are privately-owned, vehicles driven
only inside the plant are not required to undergo emissions testing. Since
these vehicles are not subject to the safety inspection and vehicle registration
program, enforcement of an inspection and maintenance program for these vehicles
would not be feasible. The commission made no changes to the rules in response
to this comment.
Waivers
One individual wanted to do away with waivers and extensions.
Waivers are a way to ensure that motorists making every "good faith" effort
to comply with I/M program requirements do not incur excessive repair costs
and/or are not excessively inconvenienced. Waivers are not extended beyond
one test cycle. Vehicle owners must meet all requirements and reapply, if
necessary, the following year to receive a new waiver for that test cycle.
The minimum expenditure waiver is available to those who have made repairs
to their vehicle within the established criteria (to include repairs made
within 60 days of an inspection) and have met the dollar limits established
by the EPA.
The commission committed to limit all waivers to no more than 3.0% in each
program area. Since the inception of the current program, the waiver rate
has not exceeded 0.4%. The commission will continue to monitor waiver rates
in all program areas. The commission made no changes to the rules in response
to this comment.
Remote Sensing
Harris County wanted to work toward utilizing remote sensing as a replacement
to tailpipe testing and expanding exemptions to a broader range of late model
cars throughout the region. In addition, one individual wanted to know why
random monitoring is ineffective in identifying gross polluters.
The commission agrees that remote sensing has a useful role to play in
detecting high-emitting vehicles in the I/M program areas. However, currently
available remote sensing technologies are not as accurate as a tailpipe test
in identifying vehicles that are near the established emissions standards.
The commission will continue to evaluate technological advances in remote
sensing to ensure the best possible testing methodologies and equipment are
considered in future program development. As remote sensing technology improves,
it may be considered for expanded use in the I/M program.
The requirement to test vehicles 2 - 24 years old is established by the
state legislature (SB 1856 of the 75th Legislature). These vehicles account
for the vast majority of vehicles on the road and the vehicle miles traveled,
which have a direct correlation to the impact on air quality. The failure
rate for vehicles less than five years old is approximately 1.0%. Because
some newer models do fail the test and because vehicles subject to the testing
are more likely to be properly maintained, the amount of emissions reductions
benefits that can be claimed for an I/M program is reduced as more model years
are exempted from the program. In addition, since many of the vehicles under
five years old are still under the manufacturer's warranty, identifying emissions-related
problems could be viewed as consumer protection and potentially may save the
vehicle's owner future repair costs. The commission made no changes to the
rules in response to these comments.
One individual felt that commuting vehicles from outlying counties driving
into Harris or Montgomery County would not be subject to inspections, but
would still be polluting the air around Houston every day.
The amended vehicle emissions testing program will require gasoline vehicles
2 - 24 years old, registered in the eight-county HGA nonattainment area to
undergo vehicle emissions testing. In addition, remote sensing will be in
operation in these counties. The remote sensing element of the vehicle emissions
testing program is operated by the DPS and is used to find high-emitting vehicles.
The commission made no changes to the rules in response to this comment.
The EPA supported the phased approach as long as non-testing counties continue
to be monitored by remote sensing for the vehicle shortfall in the testing
areas until the non-testing counties begin testing.
The I/M program will continue to use remote sensing to identify high-emitting
vehicles being operated in the nonattainment area in situations where the
number of vehicles subject to I/M program is less than the estimated fleet
in the nonattainment area. Remote sensing of commuting vehicles will continue
until the non-testing counties begin tailpipe testing all subject vehicles.
The commission made no changes to the rules in response to this comment.
Representative Zbranek, TADA, and one individual supported the expansion
of the remote sensing program to target grossly polluting vehicles.
The I/M program will continue to use remote sensing to identify high-emitting
vehicles. The commission agrees that remote sensing has a useful role to play
in detecting high-emitting vehicles in the I/M program areas.
TADA recommended that remote sensing be combined with a mandatory smoking
vehicle program to ensure that all smoking vehicles are required to be repaired
or retired.
The state-wide smoking vehicle program is a voluntary program and relies
on conscientious citizens to identify and report vehicles that they observe
emitting visible exhaust. Current remote sensing technology does not have
the ability to identify the particulate matter and sulfur compounds generally
associated with visible exhaust. Future improvements in remote sensing technology,
along with enforceable particulate standards for vehicle exhaust emissions,
may make possible such a component of the Texas program to control mobile
source emissions. The commission made no changes to the rules in response
to this comment.
One individual recommended the use of remote sensing to monitor commuting
vehicles into Harris County and if vehicles are found to be polluting, recommended
sending vehicle owners a notice that their vehicle has to be inspected.
Currently, DPS is operating three remote sensing units in Harris County
in order to monitor the emissions of vehicles commuting into the program county
from surrounding counties. Owners of vehicles identified as gross polluters
receive written notice of the violation instructing them to submit their vehicles
to an emissions test at a state-certified emissions testing station for verification
of exhaust emissions and to make necessary repairs to bring the vehicle into
program compliance. Failure to comply with written notification of an emissions
violation is a Class C misdemeanor punishable by a fine of not more than $350.
Repeat violations are punishable by a fine of not more than $1,000. The commission
made no changes to the rules in response to this comment.
ESP recommended using remote sensing (total screening) as an alternative
to I/M testing. Total screening is a combination of clean screening and high
emitter identification. Also, one individual recommended improving motorist
convenience by exempting from testing those vehicles that have demonstrated
through on-road measurements that they do not have high emissions.
The commission agrees that remote sensing has a useful role to play in
detecting high-emitting vehicles in the I/M program areas. However, the commission
believes that "clean-screening" is not a viable option at this time for the
following reasons: 1) the possibilities of false failures increase dramatically
as the cut-points for remote sensing failures are more closely aligned to
the cut-points of the tailpipe test; and 2) the cost of clean-screening depends
on many factors, such as market competitiveness, total number of remote sensing
measurements, level of automation, economies of scale, and term of contract.
According to the "California Inspection and Maintenance Review Committee Report
on Remote Sensing of Vehicle Emissions," dated September 9, 1998, a clean-screening
program that exempted 25% of the subject fleet would cost approximately $34
million per year. Although the commission believes that "clean-screening"
is not a viable option at this time, the commission will continue to evaluate
technological advances in emissions testing to ensure the best possible testing
methodologies and equipment are considered in future program development.
The commission made no changes to the rules in response to these comments.
Brazoria CCC submitted a report which concludes that remote sensing has
little practical value or use in identifying individual, dirty or clean vehicles,
that it predicts vehicle emissions at a rate less than chance and that measure
emissions with unacceptably wide variations. The report also states that remote
sensing can only view a part of the fleet. The commenter also stated that
experience and data from remote sensing in Texas show a high percentage of
inaccuracy.
The commission acknowledges the comment from Brazoria CCC. The remote sensing
program was not implemented for the purpose of replacing annual tail pipe
testing. Remote sensing is used as a non-intrusive, but efficient tool to
monitor a portion of the vehicle fleet and identify excessive polluters as
a complement to traditional mobile source emission control programs. The remote
sensing program is designed to detect potentially high-emitting vehicles registered
in or commuting into any of the affected nonattainment counties. Owners of
vehicles identified as high emitters receive written notice instructing them
to submit their vehicles to a tailpipe test at a state-certified emissions
testing station to determine compliance with emissions regulations. The commission
recognizes that remote sensing is not currently as accurate as the tailpipe
test in characterizing vehicle emissions and therefore requires identified
vehicles to submit to a confirmatory tailpipe test for validation of the remote
sensing results. The commission will continue to evaluate technological advances
in remote sensing in order to insure the best possible equipment and testing
methodologies are considered in future program development.
One individual recommended remote sensing of vehicles registered in Collin,
Denton, and Johnson Counties when driving into the city limits of Dallas,
Garland, Richardson, Carrollton, Fort Worth, Grapevine, Southlake, Burleson,
and Mansfield.
Remote sensing on highways in the DFW area to identify high-emitting vehicles
began in October 1998. Identified high-emitting vehicles may be vehicles either
registered in the designated I/M program counties (Dallas and Tarrant Counties)
or commuting from surrounding nonattainment counties (Denton and Collin Counties).
According to the vehicle emissions testing program adopted April 2000, vehicles
2 - 24 years old, registered in Dallas, Tarrant, Collin, and Denton Counties,
beginning May 1, 2002, and Johnson, Parker, Ellis, Kaufman, and Rockwall Counties,
beginning May 1, 2003, will be subject to vehicle emissions testing. In addition,
remote sensing is currently in operation in the DFW nonattainment area (Dallas,
Tarrant, Collin, and Denton Counties) and will be extended to include the
other five counties in 2003. All the cities listed in the comment are included
in the adopted DFW I/M program area. The commission made no changes to the
rules in response to this comment.
One individual advocated remote sensing of vehicles registered in Brazoria,
Fort Bend, Galveston, and Montgomery Counties, as well as when driving into
the city limits of Pearland, Houston, Katy, Missouri City, Stafford, and Friendwood
toward Central Houston.
The amended vehicle emissions testing program will require gasoline vehicles
2 - 24 years old, registered in the eight-county HGA nonattainment area to
undergo vehicle emissions tailpipe testing. In addition, the DPS will continue
to use remote sensing to identify high-emitting vehicles being operated in
the eight counties. All the cities listed in the comment are included in the
remote sensing program. The commission made no changes to the rules in response
to this comment.
One individual recommended seven requirements for prosecution if a motor
vehicle is cited for display of excess tailpipe emissions (remote sensing):
1) diesel or gasoline-powered vehicles 1979 - 1994, gasoline-powered vehicles
of model year 1978 or earlier or 1995 -2002, would be sent notices of the
need to seek repairs; 2) a peace officer from the sheriff's department, not
a constable deputy or trooper, to conduct remote sensing; 3) owner of the
motor vehicle must be served in person at his place of residence by a sheriff
deputy of the county of residence; 4) vehicle owner to be provided with the
time, date, location, and identity of driver; 5) residence of the alleged
owner of the accused motor vehicle must be in one of the seven relevant counties,
except for a truck tractor assigned to a place of business in any one of the
12 affected counties, drivers of motor vehicles of other counties/states only
would get notices of the need to seek repairs; 6) accused allowed a hearing
before a Justice of the Peace of the alleged offense with all court costs
waived; and 7) citation allowed to be make repairs to get the citation dismissed
after the first offense.
The on-road testing component of the Texas I/M program uses remote sensing
to identify high-emitting gasoline vehicles. Currently, remote sensing technology
does not have the ability to identify the particulate matter and sulfur compounds
generally associated with visible exhaust (diesels and smoking vehicles).
Future improvements in remote sensing technology, along with enforceable particulate
standards for vehicle exhaust emissions, may make possible such a component
of the Texas program to control mobile source emissions. Owners of gasoline
vehicles identified as high emitters of HC and CO receive written notice of
the violation from DPS instructing them to submit their vehicles to an emissions
test at a state-certified emissions testing station for verification of exhaust
emissions and to make necessary repairs to bring the vehicle into program
compliance. Brochures on repairing vehicles are available at each testing
station. Failure to comply with written notification of an emissions violation
is a Class C misdemeanor punishable by a fine of not more than $350. Repeat
violations are punishable by a fine of not more than $1,000.
The commission appreciates the suggestions for enforcement of the remote
sensing element of the emissions testing program, but several are outside
the commission's jurisdiction. The commission made no changes to the rules
in response to this comment.
One individual proposed that vehicle owners be allowed one of the following
options should the vehicle fail the remote sensing/emissions test: 1) to appeal
to commissioners court for assistance from an "indigent " person fund created
by increasing the license plate fee in order make repairs; 2) to sell the
vehicle (1986 or older model) to the state in a "buy back" program funded
by a local-option motor fuel sales tax of $.02 - $.05 per gallon; 3) move
to a place of residence outside of the affected counties.
The commission understands that vehicle repairs can be costly. In order
to assist the public, the vehicle emissions testing program includes two waiver
options: the minimum expenditure waiver and the individual vehicle waiver.
The minimum expenditure waiver is available to those who have made repairs
to their vehicle within the established criteria and met the dollar limits
established by the EPA rule. The individual vehicle waiver is for those who
cannot meet emissions standards despite every reasonable effort by the motorist.
In addition to these two waivers, the low income time extension is available
for those who can demonstrate a financial inability to either afford adequate
repairs or to meet the applicable minimum expenditure waiver amount. The waivers
and extension are ways to ensure that motorists who are making a "good faith"
effort to comply with the I/M program requirements do not incur excessive
repair costs, are not excessively inconvenienced, or are not denied re-registration
of their vehicle.
Enforcement of the program is the responsibility of the DPS, TxDOT, and
the commission. Vehicles registered in an I/M program area must comply with
the safety and emissions testing program (either by passing the test or qualifying
for a waiver or extension) to be issued a safety certificate. The commission,
TxDOT, and DPS implemented a vehicle re-registration denial enforcement element
for vehicles that fail to comply with the emissions testing program. Remote
sensing is used to identify high-emitting vehicles commuting into an area
and as an additional enforcement mechanism to identify high-emitting vehicles
that have not complied with the program. Once a high-emitting vehicle is identified,
the owner of the vehicle is instructed by written notice from the DPS to bring
the vehicle in to a state-certified emissions testing station for a verification
emissions test and to make necessary repairs to bring the vehicle into program
compliance. Failure to comply with the notice is a Class C misdemeanor. Local
law enforcement officials are responsible for ensuring that vehicles operating
on public roads have a valid registration sticker and safety certificate.
Provisions for a tax to create an "indigent person" or "buy back" fund
would require legislative authorization and is beyond the scope of this rulemaking.
Currently, 30 TAC Chapter 117, Tax Relief for Property Used for Environmental
Proetction, is the commission's program that provides tax relief for the purchase
of pollution control property. On November 2, 1993, the voters of Texas approved
a constitutional amendment, commonly referred to as "Proposition 2," that
provides an exemption from property taxation for pollution control property.
The intent of the constitutional amendment was to ensure that capital investment
undertaken to comply with federal, state, or local environmental mandates
did not result in an increase in a facility's property taxes. Legislation
implementing that amendment, House Bill 1920, was passed during the 73rd Texas
Legislative session which added a new §11.31 and §26.045 to the
Texas Tax Code (Tax Code). The Tax Code provides that pollution control property
could include any land purchased after January 1, 1994, or any structure,
building, installation, excavation, machinery, equipment, or device and any
attachment or addition to or reconstruction, replacement, or improvement of
property that is used, constructed, acquired, or installed wholly or partly
to meet or exceed rules or regulations adopted by any federal, state, or local
environmental agency for the prevention, monitoring, control, or reduction
of air, water, or land pollution. Motor vehicles are specifically noted as
being ineligible for an exemption under this provision of the Tax Code. The
Tax Code contains a two-step process for securing an exemption from property
taxes for pollution control property. An applicant must first receive a determination
from the commission that the property is used for pollution control purposes.
The applicant then can use this determination to apply to the local appraisal
district for a property tax exemption. The commission made no changes to the
rules in response to these comments.
Program Start-up
The Alliance, AIAM, and the EPA supported the use of OBD checks instead
of conventional I/M tests for 1996 and later model year gasoline vehicles.
The Alliance, AIAM, and the EPA recommended the OBD checks should not be used
in conjunction with I/M testing (i.e., vehicles should not be subject to both
an I/M test and an OBD check) since this would lead to unnecessary customer
confusion and frustration.
The commission concurs and adopts rules for OBD emissions testing to be
used in place of traditional tailpipe testing for 1996 and newer cars in anticipation
of the NPRM by the EPA becoming final. The EPA NPRM provides additional flexibility
by allowing states to replace the traditional I/M test on model year 1996
and newer vehicles with a check of the OBD system. Thus, the NPRM removes
the requirement to perform both a tailpipe test and OBD checks, and authorizes
OBD-only checks on 1996 and newer vehicles. In addition, the NPRM extends
implementation of OBD checks to January 1, 2002. The commission revised the
rules based on the release of the NPRM.
Program Equipment
The Sierra-Houston and one individual recommended I/M 240 centralized inspection
and maintenance tailpipe testing in conjunction with OBD testing. In addition,
three individuals would like to see a state-run test like the old IM-240.
Because the Houston nonattainment area needs to reduce NO
x
emissions, modifications to the current TSI emissions testing program
are being adopted. The ASM-2 or equivalent test, which uses a dynamometer,
is required for the HGA program area beginning in 2002. An ASM-2 type test
is estimated to achieve VOC and NO
x
emission
reductions comparable to those achieved by an IM-240 type test, but at less
than one-third of the cost, and can be implemented through the current decentralized
testing network. The EPA NPRM provides additional flexibility by allowing
states to replace the traditional I/M test on model year 1996 and newer vehicles
with a check of the OBD system. Thus, the requirement to perform both a tailpipe
test and OBD checks has been removed and OBD-only checks have been authorized
on 1996 and newer vehicles. In addition, the NPRM extends implementation of
OBD checks to January 1, 2002. The commission made no changes to the rules
in response to these comments.
One individual opposed the ASM-2 test because it is not as efficient as
the IM-240 in determining polluting vehicles. He expressed support of OBD
as an add-on to IM-240 and wants to know what is meant by "reductions comparable
to those achieved by IM-240."
The ASM-2 test achieves modeled VOC and NO
x
reductions comparable to those achieved by an IM-240 test but at less than
one-third the cost. Moreover, the ASM-2 test is considered effective in identifying
high-emitting vehicles, and can be implemented through the current decentralized
testing network. The EPA NPRM provides additional flexibility by allowing
states to replace the traditional I/M test on model year 1996 and newer vehicles
with a check of the OBD system. Thus, the requirement to perform both a tailpipe
test and OBD checks has been removed and OBD-only checks have been authorized
on 1996 and newer vehicles. In addition, the NPRM extends implementation of
OBD checks to January 1, 2002.
The phrase "reductions comparable to those achieved by IM-240" refers to
modeled emissions reductions that can be achieved using an alternative I/M
testing methodology, such as ASM-2. For example, the level of modeled emissions
reductions for the pollutant NO
x
using the ASM-2
testing method are approximately the same as the level of modeled emissions
reductions for NO
x
using IM-240. The commission
made no changes to the rules in response to these comments.
TADA supported OBD testing, but disagreed with the use of ASM-2 testing
and stated that it will be inconvenient and extremely expensive for the driving
public.
More sophisticated photochemical modeling demonstrates that the HGA area
needs to reduce NO
x
emissions in order to achieve
the ozone NAAQS. An ASM-2, or similar test, is estimated to achieve VOC and
NO
x
emission reductions comparable to those achieved
by an IM-240 type test, but at less than one-third of the cost, and can be
implemented through the current decentralized testing network which includes
over 2,300 testing facilities in the four I/M program counties (Dallas, El
Paso, Harris, and Tarrant). The test fee for a loaded mode test like ASM-2
will not be above the average for what is currently charged nationwide for
a similar test. As OBD testing is applicable only to 1996 and newer vehicles,
a tailpipe test that can measure NO
x
emissions,
such as ASM-2, must be available in order to test the pre-1996 vehicles. The
commission made no changes to the rules in response to these comments.
TADA suggested a more equitable method of paying for emissions testing
equipment is to provide a tax credit or exemption.
Provisions for a tax credit or exemption for stations owners would require
legislative authorization and is beyond the scope of this rulemaking. The
commission made no changes to the rules in response to this comment.
One individual recommended a visual check of the exhaust system should
be performed as part of the annual vehicle inspection. If an abnormality is
found, such as a loose or broken exhaust or visual smoke, the owner would
be required to have a more thorough check and repairs performed, before the
vehicle inspection is approved.
The emissions test is conducted annually in conjunction with the vehicle
safety inspection. The annual safety inspection procedures consist of a visual
exhaust emissions check on 1968 and newer vehicles. The check includes inspection
of the exhaust emission system to determine if it has been removed, disconnected
or altered in any manner to make it ineffective. If an exhaust leak is detected,
then the vehicle must be repaired before the emissions test can be conducted.
The commission made no changes to the rules in response to this comment.
One individual stated opposition to the proposed I/M program and believed
dyno testing is no better than BAR-90 testing and would like to know the effectiveness
of current program.
The commission recently completed its Mass Emissions Transient Testing
(METT) study to determine the effectiveness of the current I/M program when
compared to the EPA benchmark program for METT study. The Texas TSI I/M program
achieves about 84% HC reductions, and about 104% CO reductions, when compared
to the Arizona I/M 240 program (EPA's benchmark program). However, TSI testing
does not allow for the measurement of NO
x
because
under idle modes the temperature and pressure in the combustion chambers are
not high enough to produce a significant amount of measurable NO
x
. In order to help the HGA nonattainment area achieve the necessary
NO
x
reductions, the current tailpipe test must
be upgraded to an alternative test type, such as ASM-2 or equivalent dynamometer
test, that can measure NO
x
emissions. OBD checks
will be given to 1996 and newer model year vehicles. The commission made no
changes to the rules in response to these comments.
Repair Program
One individual wanted stricter controls and recommended a one-year warranty
on all repairs.
Establishing a one-year warranty on repairs by inspection repair shops
is beyond the scope of this rulemaking, and is outside the scope of the commission's
jurisdiction to regulate the repair industry for consumer protection. The
commission's focus is on the resulting air quality benefits measured after
the repair is completed. The commission made no changes to the rules in response
to this comment.
Program Convenience
Six individuals expressed the belief that the I/M testing program being
proposed is going to hurt those residents that have older cars that were not
built with emissions tests in mind.
Vehicles that are properly maintained should have no problem passing the
emissions test regardless of their age. Vehicles 2 - 24 years old are required
to undergo emissions testing. The cut points which determine whether a vehicle
passes or fails are calculated by factors such as the vehicle weight, model
year, and engine size. Thus, older vehicles are required to meet standards
based on criteria specific to them. The commission made no changes to the
rules in response to this comment.
Five individuals expressed opposition to the program and feel the government
is too intrusive, putting too many restrictions on consumers, that the I/M
test is too expensive, that the proposed rules go far beyond anything necessary
to protect the environment, and will be ineffective in reducing the ozone
levels.
The I/M program is one of the key strategies necessary to bring the HGA
area into attainment of the ozone standards. If the plan is unsuccessful,
the HGA area may suffer considerable economic sanctions. In addition, cleaner
air provides economic benefits to the community, such as fewer sick days,
lower medical costs, and fewer pollution-associated illnesses.
More sophisticated photochemical modeling demonstrates that the HGA area
needs to reduce NO
x
emissions in order to achieve
the ozone NAAQS. An ASM-2, or similar test, is estimated to achieve VOC and
NO
x
emission reductions comparable to those achieved
by an IM-240 type test, but at less than one-third of the cost, and can be
implemented through the current decentralized testing network which includes
over 2,300 testing facilities in the four I/M program counties (Dallas, El
Paso, Harris, and Tarrant). The test fee for a loaded mode test like ASM-2
will not be above the average for what is currently charged nationwide for
a similar test. As OBD testing is applicable only to 1996 and newer vehicles,
a tailpipe test that can measure NO
x
emissions,
such as ASM-2, must be available in order to test the pre-1996 vehicles. The
commission made no changes to the rules in response to these comments.
Program Network
Two individuals wanted to know what is wrong with the existing program.
Also, what percentage of vehicles tested under the current program failed.
Also, how much of the ozone is attributed to automobiles in the Houston area.
More sophisticated photochemical modeling demonstrates that the HGA area
needs to reduce NO
x
emissions in order to achieve
the ozone NAAQS. Although the current TSI testing program is considered effective
in identifying vehicles grossly polluting for HC or CO, idle testing does
not allow for the measurement of NO
x
. Under idle
modes the temperature and pressure in the combustion chambers are not high
enough to produce a significant amount of measurable NO
x
. This current TSI test must be upgraded to an alternative test type,
such as ASM-2, that can measure NO
x
emissions,
and therefore achieve significant NO
x
reductions.
It is estimated that 24% of the NO
x
emissions
in the HGA area are from on-road mobile sources, such as vehicles. The current
TSI emissions testing program tests vehicles 2 - 24 years old. These vehicles
account for the vast majority of vehicles on the road and the vehicle miles
traveled, which have a direct correlation to the impact on air quality. The
amount of emissions reduction benefits is not only based on repairing failed
vehicles (currently approximately 5% fail), but also from vehicles being properly
maintained because they are subject to emissions testing. The commission made
no changes to the rules in response to these comments.
Four individuals stated that the system in place now is more than adequate.
All expressed opposition to the commission reinstating a centralized IM-240
type inspection system.
The commission has no intention of mandating a centralized I/M 240 program.
However, in order to help the HGA nonattainment areas achieve the necessary
NO
x
reductions, the current TSI test must be
upgraded to an alternative test type, such as ASM-2, that can measure NO
Alliance, Houston, ESP, ExxonMobil, GEHC, Harris County, JBS, HGAC, MCA,
TCC, Phillips 66, BCCA, RAQCG, Baker Botts, Representative Madden, SPX, TABCC,
LWV-TX, EPA, and 34 individuals supported the proposed emissions testing program.
The commission appreciates the support for the vehicle emissions testing
program.
One individual stated that owners of vehicles certified as low emission
or ultra-low emission should not be penalized for living in an area with vehicles
that spew pollutants.
All vehicles certified as low emissions and ultra-low emissions should
pass the emissions test if they are properly maintained. The amount of emissions
reduction benefits is not only based on repairing failed vehicles, but also
from all vehicles being properly maintained because they are subject to emissions
testing. The commission made no changes to the rules in response to this comment.
Five individuals commented that testing vehicles on a dynamometer is a
big mistake. Cars can come off the rollers while testing causing damage to
the vehicles.
Emissions testing using dynamometers has been conducted in many states
without serious incidents being reported. Compared with the IM-240 test, where
the top speed of the car on the dynamometer is 56 miles per hour (mph), the
dynamometer's top speed will be 25 mph as prescribed by the ASM-2 type test
and the vehicle will be required to be tied down during the test. An intensive
training program will be implemented for all inspectors operating a dynamometer
type emissions test. The commission made no changes to the rules in response
to this comment.
Three individuals felt that small inspection stations will not have room
to set up this type of test or be willing to accept responsibility for accidents
on this type of equipment. In addition, three individuals expressed concern
that $40,000 is more than most inspection stations can afford.
The commission adopted the emissions test fee for the new program in order
to cover costs involved in the use of loaded mode test equipment. These costs
include labor, training, warranties, insurance, and consumable items (such
as calibration gases) used in conducting emissions tests. Based on internal
cost analysis of the proposed loaded mode testing program, the commission
approved a $22.50 emissions test fee for the new program. According to the
cost analysis study at a fee of $22.50/test, for a station to break even in
five years, based just on equipment cost of $40,000, a station must perform
about 43 emissions tests per month. For a station to break even in five years
based on equipment cost combined with an average monthly operating cost of
$1,000, a station must perform about 94 tests per month. Continued participation
in the program as it evolves will be a business decision made by each individual
station owner. The proposed ASM-2 type dynamometer can be installed above
ground in a space approximately 14 feet by 23 feet, which is the same dimensions
of most repair bays. The commission made no changes to the rules in response
to these comments.
Three individuals expressed concern that there would not be enough emission
testing facilities to test their vehicles in the counties.
The current decentralized network improved convenience over the previous
centralized network by providing more than 2,300 testing facilities in the
original four I/M program counties (Dallas, El Paso, Harris, and Tarrant).
The commission and DPS are working to ensure that the program maintains an
acceptable ratio of the subject testing fleet to emissions testing stations.
The commission made no changes to the rules in response to this comment.
One individual supported the proposed vehicle emissions testing program,
but would like to see the city-owned and government-owned vehicles tested
also.
The commission appreciates the support for the vehicle emissions testing
program. Chapter 114, §114.50(b)(7) requires state, governmental, and
quasi-governmental agencies which fall outside the normal registration or
inspection comply with all vehicle emissions I/M requirements contained in
the Texas I/M SIP for vehicles primarily operated in I/M program areas. The
commission made no changes to the rules in response to this comment.
HGAC, Houston, MCA, and 20 individuals recommended establishing a testing
program for heavy-duty diesel vehicles. One individual wanted a more thorough
and frequent stringent emissions tests for large trucks and buses (gas and
diesel) because it appears that these large trucks are the worst violators
of clean air.
Approximately 97% of the registered fleet, which is 2 - 24 years old, will
be tested using the ASM-2/OBD technology. These vehicles account for the vast
majority of vehicles on the road and the vehicle miles traveled, which have
a direct correlation to the impact on air quality. Due to equipment limitations,
heavy-duty gasoline vehicles (those vehicles over 8,500 pounds) will be tested
using the current TSI test. While the commission is currently researching
the feasibility of heavy-duty diesel vehicle testing, diesel testing is outside
the scope of this rulemaking. The commission made no changes to the rules
in response to this comment.
Two individuals stated that since vehicle manufacturers are required by
our federal government to install emissions controls on all vehicles made
to comply with federal clean air act, why is it that we now need stricter
emissions exhaust tests for state inspections?
A major contributor to air pollution is the exhaust from cars and trucks.
All over Texas vehicles contribute as much as half of the harmful air emissions
that create pollution. One vehicle in bad repair can produce 28 times as much
pollution as one vehicle in good repair. Although vehicle manufacturers are
required to install emissions controls on all vehicles, improperly maintained
emission controlled devices may eventually malfunction. The emissions testing
program tests vehicles 2 - 24 years old. These vehicles account for the vast
majority of vehicles on the road and the vehicle miles traveled, which have
a direct correlation to the impact on air quality. The amount of emissions
reduction benefit is not only based on repairing failed vehicles, but also
on vehicles being properly maintained because they are subject to emissions
testing. In addition, more sophisticated photochemical modeling demonstrates
that the HGA area needs to reduce NO
x
emissions
in order to achieve the ozone NAAQS. The TSI testing does not allow for the
measurement of NO
x
because under idle modes the
temperature and pressure in the combustion chambers are not high enough to
produce a significant amount of measurable NO
x
.
In order to help the HGA nonattainment area achieve the necessary NO
One individual stated that there are still too many heavy polluters on
our roads, particularly pick-ups, poorly maintained cars and commercial trucks.
Identifying and having these vehicles repaired will only help the HGA area
achieve the ozone NAAQS. The I/M program covers all gasoline-powered cars
and trucks regardless of size. These vehicles represent 97% of the on-road
fleet which is 2 - 24 years old. Although the current TSI testing program
is considered effective in identifying vehicles grossly polluting for HC or
CO, idle testing does not allow for the measurement of NO
x
. The current TSI test must be upgraded to an alternative test type,
such as ASM-2 with OBD, that can measure NO
x
emissions, and therefore achieve significant NO
x
reductions. The proposed ASM-2 type test is a more stringent test and estimated
to achieve VOC and NO
x
emission reductions comparable
to those achieved by an IM-240 test, but at less than one-third the cost,
and can be implemented through the same decentralized testing system as is
used for the current TSI test. In addition, remote sensing is used to identify
high-emitting vehicles. Owners of vehicles identified as high-emitters receive
written notice of the violation instructing them to submit their vehicles
to an emissions test at a state-certified emissions testing station for verification
of exhaust emissions and to make necessary repairs to bring the vehicle into
program compliance. Failure to comply with written notification of an emissions
violation is a Class C misdemeanor punishable by a fine of not more than $350.
Repeat violations are punishable by a fine of not more than $1,000. The commission
made no changes to the rules in response to this comment.
One individual wanted to install tailpipe testers on major roads to catch
the 10% of the vehicles that cause most pollution and rely on the annual test
to catch the rest.
In addition to the requirement of all gasoline-powered vehicles 2 - 24
years of age to undergo annual emissions test, remote sensing is used to identify
high-emitting vehicles commuting into an area and as an additional enforcement
mechanism to identify high-emitting vehicles that have not complied with the
program. Once a high-emitting vehicle is identified, the owner of the vehicle
is instructed by written notice from the DPS to bring the vehicle in to a
state-certified emissions testing station for a verification emissions test
and to make necessary repairs to bring the vehicle into program compliance.
The commission made no changes to the rules in response to this comment.
Five individuals wanted to see California I/M standards implemented in
Houston and six individuals wanted to see California I/M standards implemented
statewide.
The State of California is currently operating an emissions testing program
that uses the ASM-2 testing technology and will incorporate the OBD testing
technology. Modifications to the current emissions testing program in Texas
are also being adopted to include the ASM-2 testing technology, and OBD testing
technology in the designated I/M program areas. ASM-2 testing technology will
be used on 1995 and older model year vehicles. On-board diagnostic testing
technology will be used on 1996 and newer model year vehicles. Expansion of
the I/M program in all counties is beyond the scope of this rulemaking and
may require legislative authority. However, TTC, §548.301(b) and Texas
Health and Safety Code, §382.037(c) allow the commission to establish
by rule an I/M program in any county provided the county and its most populous
municipality adopt a resolution requesting such a program. The commission
has not received any such resolution to allow for implementation statewide.
The commission made no changes to the rules in response to these comments.
One individual suggested that legislation to require technological means
to clean up the dirtiest engines is be more effective and cause less disruption
of life style.
The commission does not have the authority to write legislation, but to
only enact rules based on current legislative authority. The proposed amendments
to the vehicle emissions testing program are one part of an overall clean-air
strategy for the state. Because of the scale of the HGA air quality problem
the commission is adopting a wide range of rules, including both vehicle testing
and technology solutions. The commission made no changes to the rules in response
to this comment.
Five individuals suggested a tax supported program to assist the poor in
improving their vehicles would be acceptable, if designed to minimize abuse.
Establishing a tax to assist the poor in improving their vehicles is beyond
the scope of this rulemaking and requires legislative authority. The commission
made no changes to the rules in response to this comment.
Four individuals commented that the proposed tailpipe test could not be
enforced and had too many loopholes (i.e., buying without having vehicle inspected).
Enforcement of the program is the responsibility of the DPS, TxDOT, and
the commission. Vehicles registered in an I/M program area must comply with
the safety and emissions testing program to be issued a safety certificate.
The commission, TxDOT, and DPS implemented a vehicle re-registration denial
enforcement element for vehicles that fail to comply with the emissions testing
program. In counties subject to emissions testing, owners of vehicles that
fail an emissions test and do not demonstrate proof of compliance can not
re-register or obtain their registration certificate until obtaining proof
that their vehicle complies with the emissions testing program. Remote sensing
is used to identify high-emitting vehicles commuting into an area and as an
additional enforcement mechanism to identify high-emitting vehicles that have
not complied with the program. Once a high-emitting vehicle is identified,
the owner of the vehicle is instructed by written notice from the DPS to bring
the vehicle in to a state-certified emissions testing station for a verification
emissions test and to make necessary repairs to bring the vehicle into program
compliance. Failure to comply with the notice is a Class C misdemeanor. Local
law enforcement officials are responsible for ensuring that vehicles operating
on public roads have a valid registration sticker and safety certificate.
The DPS routinely conducts covert and overt audits on inspection stations
to identify personnel fraudulently selling stickers. Personnel that are caught
are prosecuted in accordance with the law. The commission made no changes
to the rules in response to this comment.
Five individuals wanted local law enforcement agencies to strictly enforce
the new tailpipe test for automobiles and trucks.
Enforcement of the program is the responsibility of the DPS, TxDOT, and
the commission. Vehicles registered in an I/M program area must comply with
the safety and emissions testing program to be issued a safety certificate.
The commission, TxDOT, and DPS implemented a vehicle re-registration denial
enforcement element for vehicles that fail to comply with the emissions testing
program. Remote sensing is used to identify high-emitting vehicles commuting
into an area and as an additional enforcement mechanism to identify high-emitting
vehicles that have not complied with the program. Once a high-emitting vehicle
is identified, the owner of the vehicle is instructed by written notice from
the DPS to bring the vehicle in to a state-certified emissions testing station
for a verification emissions test and to make necessary repairs to bring the
vehicle into program compliance. Failure to comply with the notice is a Class
C misdemeanor. Local law enforcement officials are responsible for ensuring
that vehicles operating on public roads have a valid registration sticker
and safety certificate. The current decentralized I/M program has mechanisms
in place to prevent fraud and ensure compliance, such as referee challenge
facilities, citations, fines, registration denial, and covert audits. The
commission made no changes to the rules in response to this comment.
Five individuals stated that too many dilapidated and unsafe cars and trucks
were on the road and must be brought up to standards, taken off the road,
or scrapped.
The TTC, §502.009, states that if a vehicle has passed the safety
and emissions test it is legal for that vehicle to be driven on the road.
Motorists are issued citations by local and state law enforcement officials
for driving a vehicle with an expired or invalid state inspection certificate,
or for evading the emissions inspection or inspection outside of the affected
area. These violations of TTC, §548.602 (Class C misdemeanor) and §548.603
(Class B misdemeanor) are respectively punishable by a fine starting at $200
and not exceeding $2,000 for each occurrence. The owner will be subject to
an additional citation every time the vehicle is driven. Violators are given
notification that they must comply with the I/M program requirements. Noncompliance
will result in delivery of additional citations and fines which may accumulate
to more than the expense of a minimum expenditure waiver. For those vehicles
that fail to comply with the emissions testing program, a vehicle re-registration
denial enforcement element has been implemented. In addition, remote sensing
is used to identify high-emitting vehicles commuting into an area and as an
additional enforcement mechanism to identify high-emitting vehicles that have
not complied with the program. Once a high-emitting vehicle is identified,
the owner of the vehicle is instructed by written notice from the DPS to bring
the vehicle in to a state-certified emissions testing station for a verification
emissions test and to make necessary repairs to bring the vehicle into program
compliance. Failure to comply with the notice is a Class C misdemeanor. Ultimately,
local law enforcement officials are responsible for ensuring that vehicles
operating on public roads have a valid registration sticker and safety certificate.
Although the commission does not currently implement a scrappage program,
the commission adopted rules in April 2000 which enabled and helped define
locally run scrappage programs. The commission made no changes to the rules
in response to this comment.
One individual recommended that ample test lanes be provided and consumer
protection criteria built into the program if IM-240 is utilized.
The commission is not recommending the adoption of an IM-240 program. The
ASM-2 test for model year vehicles 1995 and older and the OBD check for model
year vehicles 1996 and newer will be offered in the decentralized test and
repair network. The commission made no changes to the rules in response to
this comment.
One individual wanted to know what happened to the "choice" in the Texas
Motorist Choice Program. We were told we would have a choice between centralized
and decentralized I/M.
The proposed amendments to the emissions testing program do not change
any of the choices motorists had under the Texas Motorists Choice Program.
The TSI testing program improved convenience by providing over 2,300 decentralized
testing facilities in the original four I/M program counties (Dallas, El Paso,
Harris, and Tarrant). This decentralized network allows motorists a choice
of test-and-repair or test-only facilities that offer the required emissions
and gas cap integrity test. Test-only facilities may offer other services
for the convenience of their customers, such as, but not limited to, oil changes,
self-serve gasoline, and any other items that are not related to automotive
parts, sales, and/or service. Test and repair facilities may offer a wide
range of repairs and services for the convenience of their customers. The
amended program will use this decentralized network to offer the same choices
to motorists. However, continued participation in the program as it evolves
will be a business decision made by each individual station owner. The commission
made no changes to the rules in response to this comment.
One individual commented that the local industry proposal is far superior
to the plan proposed by the commission.
The proposed amendments to the vehicle emissions testing program are only
one part of the regional air control strategy. In order to achieve the ozone
NAAQS, the HGA area needs to reduce NO
x
emissions.
An ASM-2, or similar test, is estimated to achieve VOC and NO
x
emission reductions comparable to those achieved by an IM-240 type
test, but at less than one-third of the cost, and can be implemented through
the current decentralized testing network. The commission made no changes
to the rules in response to this comment.
Representative Zbranek, Judge Lloyd Kirkhall of Liberty County, Senator
Bernsen, and two individuals recommended omitting Liberty and Chambers Counties
from the proposed program. Representative Zbranek also wanted the commission
and the EPA to justify why Liberty and Chambers Counties should be included
in the proposed program when modeling shows otherwise. Judge Sadler and three
individuals recommended omitting Montgomery County from the proposed I/M testing
program. The RAQCG, Harris County, and the HGAC supported the I/M program
being proposed but recommended the commission omit the counties of Chambers,
Liberty, and Waller and other appropriate counties from the I/M program based
on the small amount of mobile source emissions from these counties. In addition,
one individual made two recommendations: 1) omit Liberty County from the proposed
I/M program; and 2) to have inclusion in I/M by some other geographical boundary,
such as the border of the Trinity River or precincts which actually join Houston
and have large numbers of people that commute into Houston.
In the HGA area, eight counties have been designated as nonattainment for
the ozone NAAQS: Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty,
Montgomery, and Waller Counties. Photochemical modeling demonstrated that
reductions of both NO
x
and VOC are required over
the entire eight-county area. While the commission adopted the ASM-2 plus
OBD I/M program for all eight counties, it included a provision in the rules
to allow Chambers, Liberty, and Waller Counties the flexibility of replacing
the I/M program with an alternative control strategy, as long as the proposed
strategy achieves VOC and NO
x
reductions equivalent
to those from the I/M program. The concept of redefining the I/M program area
by geographical boundaries would prove very difficult to implement, especially
due to the focus on county of registration in the program enforcement.
Missouri City wanted to know if its city vehicles are exempt from additional
inspection and from additional test fees.
The vehicle I/M program requires annual testing of all gasoline-powered
motor vehicles (including city and state-owned vehicles and leased vehicles)
that are 2 - 24 years old, primarily operated and registered, or required
to be registered, in the affected counties. There is no exemption for government
vehicles. The commission made no changes to the rules in response to this
comment.
One individual generally supported the program but recommended mandatory
emissions testing every three years.
The commission appreciates the support of the vehicle emissions testing
program. Vehicle emission testing is an integral part of the total air control
strategy. Emission reduction credits achieved by any type of I/M program are
reduced significantly when the program is not implemented as an annual test.
The commission made no changes to the rules in response to this comment.
One individual recommended allowing individuals to report license plate
numbers from smoking vehicles to a police computer. After three reports, a
letter would be sent out instructing the motorist to bring the vehicle in
for testing. If the vehicle passes the inspection, the inspection is free.
If the vehicle fails, the owner is charged an inspection fee and given 30
days to fix, repair, sell, retire, or destroy the vehicle.
The commission implements a state-wide smoking vehicle program which relies
on conscientious citizens to identify and report vehicles that they observe
emitting visible exhaust. Citizens may report vehicles by an established hotline
(1-800-453-SMOG(7664)) or through the WEB at WWW.SMOKINGVEHICLE.ORG. Letters
and informational brochures on causes of excessive smoke are sent to vehicle
owners encouraging them to have their vehicle checked, and if necessary, repaired.
The commission does not plan to change this program at this time. The commission
made no changes to the rules in response to this comment.
One individual recommended that vehicle inspection facilities be open 24
hours a day.
There are currently more than 2,300 emissions testing facilities in the
original four I/M program counties (Dallas, El Paso, Harris, and Tarrant).
According to DPS safety and emissions station requirements, an inspection
station must be open at a minimum of 40 hours per week. The actual operational
hours are a business decision made by each individual station owner and are
outside the scope of this rulemaking. If there is a demand for after hours
testing the commission expects that the market would respond. However, it
would not be reasonable to require every station to provide this service.
The commission made no changes to the rules in response to this comment.
SPX supported the proposed ASM-2/OBD testing program with the following
provisions: implement the enhanced I/M program as soon as possible in all
areas; test fees should be market driven; continue the proposed program for
a minimum of five years; commission specify that BAR-97 certification be a
minimum requirement for companies providing equipment to the new program;
and use on-road remote sensing as one of the tools the commission will use
for program evaluation. In addition, TADA commented that a market-based fee
system would be appropriate if ASM-2 testing is adopted.
The commission is adopting a phased approach to make for a smooth implementation
while still providing significant air quality improvements. ASM-2 and OBD
testing will be implemented in Harris, Dallas, Tarrant, Denton, and Collin
Counties beginning May 1, 2002; in Brazoria, Fort Bend, Galveston, Montgomery,
Ellis, Johnson, Kaufman, Parker, and Rockwall Counties beginning May 1, 2003;
and in Chambers, Liberty, and Waller Counties beginning May 1, 2004.
The commission believes a fixed fee to be more equitable across the market
place by allowing for consistency of price within program areas and provides
consumer protection. The commission made no change to these rules.
An emissions testing program is required by federal law and has been authorized
to be implemented through Texas state law. The program is subject to change
based on changes that could occur in the federal and/or state laws which authorized
the current program. Because the program is subject to this authorization,
the commission cannot guarantee the program for any set amount of time. Purchasing
new testing equipment is a business decision and is the responsibility of
the buyer at any given point in time to determine if an investment in an analyzer
is worth the cost. Furthermore, as technology evolves over time, the commission
will continue to evaluate technological advances in emissions testing to ensure
the best possible testing methodologies and equipment are considered in future
program development.
The commission concurs with the minimum requirement for all companies to
submit proof that the test equipment which they plan to provide as a part
of the new program has received BAR97 certification. The specifications for
test equipment used in the new program contain this requirement.
Remote sensing is an integral part of the I/M program. Although it is not
used as part of the program evaluation, it is used to capture the requirement
of on-road testing and used to identify high-emitting vehicles registered
in the designated I/M program areas. The current method that is used by staff
for I/M program evaluation is the EPA-approved Sierra Research method for
METT. The commission will continue to evaluate technological advances in methods
for I/M program evaluation.
The commission made no changes to the rules in response to these comments.
SPX stated that the alternative test procedures study completion date may
be too late to have an impact on program design decisions and recommended
that the study be completed sooner or abandoned in favor of a generally accepted
I/M program design.
The commission is conducting a study that will evaluate the use of an alternative
test procedure. The scheduled completion date for the study is February 2001.
The commission believes that this date will provide sufficient time to implement
any necessary program changes. The commission made no changes to the rules
in response to this comment.
TADA commented that small business owners will decline to participate in
an ASM-2 program because the equipment is more expensive, higher wages will
have to be paid for more qualified inspectors, and insurance and liability
claims will increase due to dynamometer testing. In addition, Judge Sylvia
of Chambers County expressed concern that the proposed I/M program will place
a heavy burden on his constituents. Judge Sylvia also expressed concern that
there will not be enough testing stations that can afford the $40,000 for
new equipment and enough testing stations to perform the emissions test.
The commission adopted a fee of $22.50 for both the ASM-2 and OBD tests
in order to cover costs involved in the use of loaded mode test equipment.
These increased costs include labor, training, warranties, insurance, and
consumable items (such as calibration gases) used in conducting emissions
tests. Continued participation in the program as it evolves will be a business
decision made by each individual station owner. However, staff are in discussion
with analyzer manufacturers to identify ways to relieve the economic burden
for inspection station operators at the outset of the program. The commission
made no changes to the rules in response to these comments.
Representative Madden generally supported the program, but made two comments
regarding the proposed I/M program. First, Representative Madden did not want
to have any contractual obligations as the state had with the previous testing
contractor, Tejas. Second, he wanted to ensure that there will time to evaluate
the vehicle test project now in the DFW area and included in the SIP area
so that there will be flexibility to modify the requirement of better testing
methods for NO
x
produced or if the same results
are produced by a less costly test method.
The commission has no intention of contracting with one company to implement
a centralized testing system as was the case with the original IM-240 program.
The I/M program will continue to be implemented using a decentralized network
comprised of individual inspection station owners. However, some specialized
portions of the program such as remote sensing and computerized data management
are currently contracted out. These contracts do not approach the magnitude
of the Tejas contracts.
The commission included flexibility in the rules and SIP to change the
testing methodology based on the results of the vehicle technology testing
project if the alternative testing technology proves to be as or more effective
than the proposed ASM-2 testing methodology in identifying vehicles with excessive
NO
x
emissions. The commission believes there
will be sufficient time to do this, decided, before the first implementation
date of May 1, 2002. The commission made no changes to the rules in response
to these comments.
One individual recommended that owners of polluting vehicles pay a stiff
fine for driving on city streets.
Vehicles registered in an I/M program area must comply with the safety
and emissions testing program to be issued a safety certificate. Motorists
are issued citations by local and state law enforcement officials for driving
a vehicle with an expired or invalid state inspection certificate. These violations
of the TTC, §548.602 (Class C misdemeanor) and §548.603 (Class
B misdemeanor) are respectively punishable by a fine starting at $200 and
not exceeding $2,000 for each occurrence. The owner is subject to a possible
additional citation every time the vehicle is driven. Violators are given
notification that they must comply with the I/M program requirements. Noncompliance
will result in delivery of additional citations and fines. In addition, remote
sensing is used to identify high-emitting vehicles commuting into an area
and as an additional enforcement mechanism to identify high-emitting vehicles
that have not complied with the program. When a high-emitting vehicle is identified,
the owner of the vehicle is instructed by written notice from the DPS to bring
the vehicle in to a state-certified emissions testing station for a verification
emissions test and to make necessary repairs to bring the vehicle into program
compliance. Failure to comply with the notice is a Class C misdemeanor. Local
law enforcement officials are responsible for ensuring that vehicles operating
on public roads have a valid registration sticker and safety certificate.
According to the TTC, Chapter 548, vehicles failing to have a valid safety
and emissions certificate could range from a Class C misdemeanor to a second
degree felony, based on the charge. The fine could range from $200 to $10,000
and potentially involve confinement in a state jail. The commission made no
changes to the rules in response to this comment.
One individual recommended the commission avoid proposals not based on
proven technologies i.e., tailpipe testing.
The commission is adopting a tailpipe test method that is accepted by the
EPA through research conducted by the National Center for Vehicle Emissions
Control and Safety at Colorado State University. The I/M program checks whether
the emission control system on a vehicle is working correctly. All new passenger
cars and trucks sold in the United States today must meet stringent pollution
standards, but they can only retain this low-pollution profile if the emission
controls and engine are functioning properly. The I/M program is designed
to ensure that vehicles stay clean in actual consumer use. Through annual
vehicle emissions inspection and required repairs for vehicles that fail the
test, the I/M program encourages proper vehicle maintenance and discourages
tampering with emission control devices. I/M programs have been implemented
for many years and the technology has been proven effective.
State Compliance
One individual in Liberty County suggested that the current program has
only a 40% compliance rate.
Current I/M program data and a 1996 vehicle safety inspection sticker compliance
rate survey for Dallas, El Paso, Harris, and Tarrant Counties (Appendix J
of the SIP) suggests a compliance rate of approximately 96%. The commission
will continue to monitor the program's compliance rate.
Motorist Compliance
Two individuals commented that stricter exhaust emission checks are just
another way to pay more money for inspection stickers and squeeze revenue
from the consumer. They believed most vehicles will pass anyway and for those
that fail, there are plenty of places that will pass you for an extra $10
under the table.
More sophisticated photochemical modeling demonstrates that the HGA area
needs to reduce NO
x
emissions in order to achieve
the ozone NAAQS. The current TSI test does not identify NO
x
emissions because under idle modes, the temperature and pressure
in the combustion chambers are not high enough to produce a significant amount
of measurable NO
x
. In order to help the HGA nonattainment
area achieve the necessary NO
x
reductions, the
current tailpipe test must be upgraded to an alternative test type, such as
ASM-2, that can measure NO
x
emissions. OBD checks
will be given to 1996 and newer model year vehicles. An ASM-2, or similar
test, is estimated to achieve VOC and NO
x
emission
reductions comparable to those achieved by an IM-240 type test, but at less
than one-third of the cost, and can be implemented through the current decentralized
testing network which includes over 2,300 testing facilities in the four I/M
program counties (Dallas, El Paso, Harris, and Tarrant). The test fee for
a loaded mode test like ASM-2 will not be above the average of what is currently
charged nationwide for a similar test. As OBD testing is applicable only to
1996 and newer vehicles, a tailpipe test, such as ASM-2, must be available
in order to test the pre-1996 vehicles.
A major contributor to air pollution is the exhaust from cars and trucks.
All over Texas vehicles contribute as much as half of the harmful air emissions
that create pollution. One vehicle in bad repair can produce 28 times as much
pollution as one vehicle in good repair. Even though vehicle manufacturers
are required to install emissions controls on all vehicles, improperly maintained
emissions controlled devices may eventually malfunction. The amount of emissions
reduction benefit is not only based on repairing failed vehicles, but also
on vehicles being properly maintained because they are subject to emissions
testing.
To combat fraud and abuse in the emissions testing program, mechanisms
are in place to prevent fraud and ensure compliance, such as referee challenge
facilities, citations, fines, registration denial, and covert and overt audits
of inspection stations.
The commission made no changes to the rules in response to these comments.
Two individuals recommended deleting the visual examination (parameter
check) to verify that certain factory equipment remains installed on the vehicle.
In addition, the visual examination prevents the car owner from improving
on the original design of the car and further reducing emissions and/or improving
fuel economy.
Vehicle configurations are certified by the EPA. The FCAA, §203(a)(3)
(42 USC, §7522(a)(3)), "prohibits any person from removing or rendering
inoperative any emission control device or element of design installed on
or in a motor vehicle or motor vehicle engine prior to its sale and delivery
to an ultimate purchaser" and prohibits "any person from knowingly removing
or rendering inoperative any such device or element of design after such sale
and delivery to the ultimate purchaser." The visual check is an important
part of the vehicle safety inspection. The commission made no changes to the
rules in response to these comments.
One individual recommended that all vehicles operating in or commuting
into all nonattainment areas be subject to a more stringent test and issued
a corresponding "distinctive" sticker.
Vehicles within the designated I/M program areas have a distinctive bar
on the vehicle's registration sticker to identify that the vehicle is registered
in the program area and therefore subject to an emissions test. All 2 - 24
year old gasoline-powered vehicles registered in an I/M program area, as well
as vehicles that operate more than 60 calender days per testing cycle in an
I/M program area, are required to comply with emissions standards for such
an area. Vehicles must comply with the safety and emissions testing program
to be issued a safety certificate. As an additional enforcement mechanism,
remote sensing is used to identify high-emitting vehicles operating in an
I/M program area. Once a high-emitting vehicle is identified, the owner of
the vehicle is instructed by written notice to bring the vehicle in to a state-certified
emissions testing station for a verification emissions test and to make necessary
repairs to bring the vehicle into program compliance. Vehicles registered
outside the nonattainment areas are not subject to emissions testing. The
commission made no changes to the rules in response to this comment.
Six individuals wanted to see obvious oil burning or ill-maintained vehicles
stopped and cited when on the freeway. It was also recommended that after
a citation has been issued, a five-day retractable grace period be implemented,
if the motorist brings the vehicle back into compliance.
The TTC, §548.306, specifies that a motor vehicle registered in an
ozone nonattainment area commits an offense if visible smoke remains suspended
in the air ten or more seconds before fully dissipating. Therefore, law enforcement
personnel may issue a citation to the registered owner of a vehicle that produces
excessive visible smoke. A law enforcement officer who has probable cause
to believe that this offense has been committed, has the authority to issue
the driver of the vehicle an informative citation and explain that the registered
owner of the vehicle may receive notice in the mail about the violation. 30
TAC §111.111(a)(5) states that motor vehicles shall not have visible
exhaust emissions for more than ten consecutive seconds. This rule applies
statewide and can be enforced by local law enforcement agencies. Implementing
a five-day grace period after the citation has been issued is beyond the scope
of this rulemaking. The commission made no changes to the rules in response
to these comments.
One individual recommended that a program be established to find older
cars without smog devices and people who disable their catalytic converter.
According to the "Rules and Regulations Manual for Operation of Official
Vehicle Inspection Stations" the annual safety inspection procedures consist
of a visual exhaust emissions check on 1968 and newer vehicles. The check
includes inspecting the exhaust emission system to determine if it has been
removed, disconnected, or altered in any manner to make it ineffective; checking
the plumbing or hoses for leaks, breaks, and improper routing; and checking
the air pump (air injection type) to determine if it is loose, broken, excessively
cracked, frayed, or has pieces missing. The inspector also checks the catalytic
converter on 1984 or later model vehicles to make sure it has not been removed
or is leaking or disconnected. The commission made no changes to the rules
in response to this comment.
Three individuals wanted to incorporate mandatory inspections prior to
registration of the vehicle.
Incorporating mandatory inspections prior to registration of the vehicle
requires legislative authority and is therefore beyond the scope of this rulemaking.
Currently, motorists whose vehicle have failed the emissions test and have
not complied with the I/M program requirements are denied re-registrations
of the subject vehicle until the motorist has complied with the I/M program
requirements. The commission made no changes to the rules in response to this
comment.
ExxonMobil, LWV-TX, BCCA, and two individuals supported ASM-2 testing with
integrated OBD testing in all eight counties of the HGA.
The commission appreciates the support of OBD and ASM-2 testing and agrees
that emissions reductions of NO
x
and VOCs are
required from all eight counties for the HGA area to demonstrate ozone attainment.
The Liberty County Sheriff asked who is going to enforce the regulation?
The vehicle emissions testing program is administered under Texas state
law by the commission, TxDOT, and the DPS. Vehicles registered in an I/M program
area must comply with the safety and emissions testing program to be issued
a safety certificate. Motorists can be issued citations by local and state
law enforcement officials for driving a vehicle with an expired or invalid
state inspection certificate, or for evading the emissions inspection or inspection
outside of the affected area. These violations of the TTC, §548.602 (Class
C misdemeanor) and §548.603 (Class B misdemeanor) are respectively punishable
by a fine starting at $200 and not exceeding $2,000 for each occurrence. Violators
are given notification that they must comply with the I/M program requirements.
The commission, TxDOT, and DPS implement a vehicle re-registration denial
enforcement element for vehicles that fail to comply with the emissions testing
program.
Remote sensing is used to identify high-emitting vehicles commuting into
an area and as an additional enforcement mechanism to identify high-emitting
vehicles that have not complied with the program. Once a high-emitting vehicle
is identified, the owner of the vehicle is instructed by written notice from
the DPS to bring the vehicle into a state-certified emissions testing station
for a verification emissions test and to make necessary repairs to bring the
vehicle into program compliance. Failure to comply with the notice is a Class
C misdemeanor. Local law enforcement officials are responsible for ensuring
that vehicles operating on public roads have a valid registration sticker
and safety certificate.
DPS also conducts overt and covert audits of the vehicle inspection stations.
One individual recommended sticking to the existing program.
The current TSI testing program is considered effective in identifying
vehicles grossly polluting for HC or CO. However, idle testing does not allow
for the measurement of NO
x
because under idle
modes the temperature and pressure in the combustion chambers are not high
enough to produce a significant amount of measurable NO
x
. In order to help the HGA nonattainment area achieve the necessary
NO
x
reductions, the current TSI test must be
upgraded to an alternative test type, such as ASM-2 that can measure NO
Geographic Coverage
The Sierra-Houston and seven individuals supported tougher auto emissions
testing and felt that all counties should be subject to this rule and enforced
statewide. LWV-TX commented that testing should be required throughout the
airshed.
Expansion of the I/M program in all counties is beyond the scope of this
rulemaking and may require legislative authority. However, TTC, §548.301(b)
and Texas Health and Safety Code, §382.037(c) allow the commission to
establish by rule an I/M program in any county provided the county and its
most populous municipality adopt a resolution requesting such a program. The
commission has not received any such resolutions to allow for implementation
statewide. The commission made no changes to the rules in response to these
comments.
One individual recommended tailpipe testing for all vehicles registered
by residences of the following cities: Dallas, Garland, Richardson, Carrollton,
Coppell, Fort Worth, Grapevine, Southlake, Burleson, Mansfield, Pearland,
Houston, Katy, Missouri City, Stafford, and Friendwood.
Residents of Dallas (Collin, Dallas, Denton, Kaufman, and Rockwall Counties);
Garland (Collin, Dallas, and Rockwall Counties); Richardson (Collin and Dallas
Counties); Carrollton (Collin, Dallas, and Denton Counties); Coppell (Dallas
and Denton Counties); Fort Worth (Tarrant and Denton Counties); Grapevine
(Dallas, Denton, and Tarrant Counties); Southlake (Denton and Tarrant Counties);
Burleson (Johnson and Tarrant Counties); Mansfield (Ellis, Johnson, and Tarrant
Counties); Pearland (Brazoria and Harris Counties); Houston (Fort Bend, Harris,
and Montgomery Counties); Katy (Fort Bend, Harris, and Waller Counties); Missouri
City (Fort Bend and Harris Counties); Stafford (Fort Bend and Harris Counties);
and Friendswood (Galveston and Harris Counties) are all in affected counties
and will be required to have emissions tests conducted on their registered
vehicles. The commission made no changes to the rules in response to this
comment.
One individual recommended tailpipe testing for residents in Plano, the
Colony, Flower Mound, Lewisville, Corinth, Denton, Lake Dallas Shores, Dickinson,
League City, New Caney, Porter, The Woodlands, and Oak Ridge North prior to
acquisition of new plates for: 1) diesel-powered motor vehicles; 2) gasoline
vehicles model years 1979 - 1994 registered with new plates starting in 2002;
3) gasoline vehicles model years 1995 - 2002 which are repaired after collisions;
and 4) out-of-state residents receiving Texas license plates.
All 2 - 24 year old gasoline-powered vehicles registered in the program
area must comply with the safety and emissions testing program to be issued
a safety certificate. A phased approach to implementing the I/M program has
been adopted by the commission which will include all of the cities listed.
Currently, diesel-powered vehicles are not included in the I/M program.
These vehicles make up a small percentage (approximately 3%) of the vehicle
population. Due to less standardization in diesel vehicles, more technological
development is needed before testing is initiated. The commission is, however,
researching the future feasibility of diesel testing.
All vehicles are tested annually whether in an accident or not. In addition,
most collisions do not necessarily impair vehicle emissions equipment. Motorists
who relocate to Texas from out-of-state must pass a safety inspection prior
to registering their vehicle in Texas. Also, if the motorist resides in an
I/M program area, they are required to comply with the safety and emissions
requirements before receiving Texas plates.
The commission made no changes to the rules in response to these comments.
Other Issues
One individual commented that Texas consider alternative means, such as
those taken recently by Florida, of dealing with air pollution that do not
interfere with every individual.
The air quality in the nonattainment areas in Florida has improved enough
to have the areas classified as attainment areas in 1994. The vehicle emissions
testing program in Florida was a voluntary measure by the Florida Legislature
to ensure continued compliance with the air quality standards. Later, Florida's
state implementation plan indicated that the state could demonstrate continued
compliance with the air quality standards without using tailpipe testing as
a control strategy. Therefore, the Florida Legislature had the option of eliminating
their emissions testing program. Since the Houston area cannot demonstrate
compliance with the air quality standards, vehicle emissions testing must
continue to be one of the many control strategies used in Texas. The commission
made no changes to the rules in response to this comment.
Three individuals felt that tailpipe testing would do no good.
A major contributor to air pollution is the exhaust from cars and trucks.
All over Texas vehicles contribute as much as half of the harmful air emissions
that create pollution. One vehicle in bad repair can produce 28 times as much
pollution as one vehicle in good repair. Even though vehicle manufacturers
are required to install emissions controls on all vehicles, if the vehicles
are not being properly maintained, the emissions control devices will be less
effective. The emissions testing program tests vehicles 2 - 24 years old.
These vehicles account for the vast majority of vehicles on the road and the
vehicle miles traveled, which have a direct correlation to the impact on air
quality. The amount of emissions reduction benefits is not only based on repairing
failed vehicles, but also from vehicles being properly maintained because
they are subject to emissions testing. As OBD testing only applies to model
year 1996 and newer vehicles, there is a need for a tailpipe test to identify
high NO
x
emissions from older vehicles. The commission
made no changes to the rules in response to this comment.
GEHC supported tougher programs for testing vehicles emissions but not
until obvious changes have taken place to stop grandfathered and industrial
pollution.
The commission has made no change in response to the comments. The implementation
of the vehicle emissions program is one of many programs being adopted to
reduce ozone. The commission's plan to reduce ozone pollution also includes
programs designed to achieve significant reductions from industrial and manufacturing
facilities. Combined, these programs provide the best plan for achieving the
necessary reductions without overburdening any one sector of the community.
The adopted rules that apply to facilities, for example the Chapter 117
NO
x
requirements and the Chapter 115 VOC requirements,
apply to both permitted and non-permitted ("grandfathered") sources in HGA.
The commission agrees that it is appropriate to pursue cost-effective measures
to reduce pollution; however, any such measures must be within the statutory
authority of the commission. The TCAA does not authorize the commission to
require grandfathered sources to obtain permits in order to operate, or to
prohibit operation of those sources. A grandfathered facility is one that
existed at the time the Texas Legislature amended the TCAA in 1971. These
facilities were not required to comply with (i.e., were grandfathered from)
the then new requirement to obtain permits for construction activities. Whenever
a grandfathered facility is modified (as that term is defined in the TCAA)
then it is required to comply with the TCAA permitting requirements in order
to be authorized to construct and operate that modification. If a grandfathered
facility has never been modified, it continues to be authorized by the TCAA
to operate without a permit. Further, the definition of "modification" specifically
excludes changes to facilities that are authorized by an exemption, i.e.,
any facility, including a grandfathered facility, can make a change using
a commission exemption (now permit by rule) and this change is not considered
to be a modification that would trigger the permitting requirements of the
TCAA. During the 76th Texas Legislative Session in 1999, the issue of grandfathered
sources was addressed by two different legislative programs. Senate Bill 766
was passed which provided a framework for a voluntary permitting program for
grandfathered sources under the TCAA, and SB 7 which requires mandatory permitting
and emission reductions from electric generating facilities. The commission
continues to pursue enforcement action against companies who are not in compliance
with the permitting requirements of the TCAA. However, Senate Bill 766 does
provide for amnesty from enforcement for facilities eligible to participate
in the voluntary emission reduction permit program as long as a permit application
is received before the TCAA deadline of September 1, 2001.
Brazoria CCC commented that the impact of the emissions testing and denial
of re-registration of vehicles who do not pass the test has a disparate impact
upon the economically disadvantaged citizens. The commenter stated that this
denial of the right to use a vehicle is a taking of property without a hearing
and without compensation. The commenter stated that the procedures contained
in the SIP constitute an unlawful delegation of legislative authority to an
administrative agency.
Although it is not clear what, if any, legal standard the commenter alleges
the commission would violate in adopting the rules, they state that the rules
would "disproportionately impact" economically disadvantaged. This could be
a reference to Title VI of the Civil Rights Act of 1964. In order for the
commission to be shown in violation of Title VI, a disproportionately negative
impact to minorities must be shown. The commission maintains that the rules
as adopted will not have a disparate impact on persons based on race, color,
or national origin. The basis for the rules is protection of human health
and the environment, and the reduction in overall motor vehicle emissions
is anticipated to provide reductions in the formation of ozone in the area.
As for potential negative impacts of the rules, these are clearly borne equally
by all drivers governed by the rules without any differentiation by race,
color, or national origin.
The commission understands that vehicle repairs can be costly. In order
to assist the public, the vehicle emissions testing program includes two waiver
options: the minimum expenditure waiver and the individual vehicle waiver.
The minimum expenditure waiver is available to those who have made repairs
to their vehicle within the established criteria and met the dollar limits
established by the EPA rule. The individual vehicle waiver is for those who
cannot meet emissions standards despite every reasonable effort by the motorist.
In addition to these two waivers, the low-income time extension is available
for those who can demonstrate a financial inability to either afford adequate
repairs or to meet the applicable minimum expenditure waiver amount. The waivers
and extension are ways to ensure that motorists who are making a "good faith"
effort to comply with the I/M program requirements do not incur excessive
repair costs, are not excessively inconvenienced, or are not denied re-registration
of their vehicle.
With regard to the idea that the program amounts to a taking of a vehicle,
the commission disagrees with the commenter. Legally, this program is no different
than the requirement that all drivers must carry liability insurance in order
to operate their vehicle. While both programs set conditions which must be
met before operating a motor vehicle, the state's police power to protect
the health and safety of the general public outweighs the burden on the individual
driver. Neither program represents a taking of a vehicle without hearing or
just compensation.
Finally, the I/M program is not an unlawful delegation of legislative authority
to an administrative agency. The Texas Legislature has defined and redefined
the parameters of an authorized I/M program over the past decade. The current
specific state authorization is found in the TCAA, §§382.037 - 382.038.
Additionally, the directive of the legislature to adopt a program as required
by federal law, TCAA, §382.037(c)(1), was written in light of the specific
federal program requirements found in FCAA, §182(c)(3) and in EPA rules
at 40 CFR Part 51, Subpart S. The I/M program has been lawfully authorized
and the implementation of the program lawfully delegated to the commission.
Brazoria CCC commented that the remote sensing component of the program
is a violation of the United States Constitution because it is covert surveillance
of citizens without probable cause. Brazoria CCC stated that the proposed
program violates the United States Constitution as it pertains to criminalizing
innocent behavior and not affording the presumption of innocence, as well
as proposing enforcement tactics that clearly violate the safeguards of probable
cause in the criminal justice system.
The commission disagrees with the commenter that the remote sensing component
of the program amounts to an illegal search. The remote sensing components
detects emissions of vehicles which are operating on the public roadway in
plain view and therefore is not a search. There is no unlawful entry into
private domain and the vehicle is not stopped at the time of the test so there
is no seizure. Further, as case law indicates, there is a reduced expectation
of privacy associated with motor vehicles and therefore only probable cause
is required to search an automobile.
The commission disagrees with the commenter's assertion that the program
criminalizes innocent behavior. It is not a crime to be detected as a high-emitter
by remote sensing equipment so there is no presumption of guilt or innocence.
In the event that a vehicle detected as a high-emitter, the operator is required
to bring the vehicle in for an emission test. The operator may choose to repair
the vehicle before bringing it for a test, in which case a clean test will
mean there are no further conditions upon that operator. If the operator then
fails the emission test, the operator must either repair the vehicle or qualify
for a waiver within a certain period of time. It is only the operator who
does not bring the vehicle in at all or who does not follow-up after a failed
test who is subject to penalty under the program. In these cases, probable
cause has clearly been demonstrated and due process is provided through the
enforcement phase.
One individual commented that the proposed I/M program was illegal, unconstitutional,
and unenforceable. In addition, he wanted to know if he will be considered
a criminal for driving a vehicle that cannot pass a tailpipe test.
The FCAA Amendments of 1990 require vehicle emission testing in all communities
where ozone levels exceed federal health standards which have been classified
as moderate or above nonattainment areas. Senate Bill 1856, passed by the
Texas Legislature, 75th Session, 1997, gave the commission the authority to
establish the current I/M program.
The vehicle emissions testing program is administered under Texas state
law by the commission and the DPS. The TTC, §548.301, states that the
commission shall establish a motor vehicle emissions inspection and maintenance
program for vehicles as required by any law of the United States or the state's
air quality state implementation plan. The TCAA, §382.037, specifies
that the commission by rule may require emissions-related inspection and maintenance
of land vehicles, including testing exhaust emissions, examining emission
control devices and systems, verifying compliance with applicable standards,
and other requirements as provided by federal law or regulation. Motorists
are issued citations by local and state law enforcement officials for driving
a vehicle with an expired or invalid state inspection certificate, or for
evading the emissions inspection or inspection outside of the affected area.
These violations of the TTC, §548.602 (Class C misdemeanor) and §548.603
(Class B misdemeanor) are respectively punishable by a fine starting at $200
and not exceeding $2,000 for each occurrence. The owner will be subject to
an additional citation every time the vehicle is driven. Violators are given
notification that they must comply with the I/M program requirements.
Although it is a criminal offense to drive a vehicle without a proper safety
and emissions certificate, it is not a criminal offense to drive a vehicle
that has not passed the emissions test if the vehicle has received a waiver
or extension.
The commission disagrees with the commenter's statement that the I/M program
is unconstitutional for all the reasons stated in response to comments regarding
unlawful taking, due process, unlawful delegation.
The commission made no changes to the rules in response to these comments.
Baker Botts commented that it generally supports the ongoing efforts by
the commission to develop a SIP that is technologically achievable, economically
reasonable, and legally approvable. Baker Botts, BCCA, ExxonMobil, Harris
County Judge Robert Eckels, Phillips 66, TCC, and an individual commented
that the commission should incorporate into the SIP a greater level of reductions
from federally preempted sources and stated that EPA-regulated sources account
for about 40% of the NO
x
emissions in the HGA.
The commenters stated that the EPA issued a number of regulations for some
federally preempted sources, such as land-based spark engines, marine, recreational
and land-based diesel engines, aircraft and locomotive engines, well after
the FCAA deadlines, and that the EPA recently strengthened rules for on-road
and non-road vehicles and fuels, such as low sulfur gas and diesel, Tier II
motor vehicles, heavy-duty highway vehicle standards, and non-road Tier II/Tier
III heavy-duty engine standards. The commenters stated that delays in implementing
these rules have prompted the commission to propose technically and economically
infeasible emission reductions from sources in HGA that the state has authority
to regulate to make up for the missing federal reductions. The commenters
stated that these delays have forced the commission to propose expensive regional
fuels and significant use restriction regulations. The commenters stated that
the commission and the EPA can ensure an equitable distribution of the compliance
burdens necessary to meet mandated air quality improvement in HGA only by
allowing the SIP to capture anticipated emission reductions from federally
preempted sources. Baker Botts noted that the EPA demonstrated a willingness
to assume responsibility for a portion of emission reductions by creating
a process in Los Angeles called a "public consultative process," that would
resolve issues related to emissions from national and international sources,
and that the EPA has also provided flexibility in obtaining offsets by allowing
states to provide offsets to refiners based on emission reductions that the
EPA projected would result from mobile sources using Tier II gasoline. Baker
Botts suggested that this same sort of prospective crediting should be used
to develop a more rational HGA SIP, and that the EPA should allow the commission
to credit in the SIP the prospective emission reductions that will result
from implementation of the Tier II gasoline rule and from other federally
preempted sources. Finally, Baker Botts cited two cases wherein the District
of Columbia Circuit has approved the EPA's flexibility with respect to statutory
deadlines under the FCAA when the EPA has failed to meets its own deadlines,
and this failure was deemed to upset the balanced federal/state responsibilities
under the FCAA. ExxonMobil commented that it supports the commission and the
EPA crediting the HGA SIP with an additional 60 tpd of federally preempted
emission reductions that will occur over the next ten years. Harris County
Judge Robert Eckels commented that the commission should work with the EPA
to accelerate the implementation schedule for federally preempted emissions
so that at least one-half of the related emission reductions are achieved
by 2007, and that as a part of this process, the commission should delineate
federal assignments detailing the engine standards and emission reductions
necessary to achieve real and sustainable pollution reductions.
The commission agrees with the commenters that emission reductions from
federally preempted sources would provide benefits for the HGA SIP demonstration,
and the inability of the commission to regulate certain source categories
has necessitated the use of other ozone control strategies. However, the commission
understands that the EPA SIP approval process does not provide a mechanism
for credit for emission reductions that occur after the attainment date. The
commission understands that EPA is not currently considering accelerating
implementation schedules for existing federal rules. The commission is working
with EPA to determine the availability of SIP credit for many non-traditional
control strategy mechanisms, like economic incentive programs and flexibility
for preempted source categories. Additionally, the commission is working with
EPA to determine an appropriate federal contribution credit available for
the HGA SIP.
BCCA, ExxonMobil, and Phillips commented that the commission has failed
to follow the requirements for adopting a major environmental rule as required
by Texas Government Code, §2001.0225 (i.e. no cost benefit analysis performed;
no draft impact analysis performed; no description of why identified reasonable
alternative were rejected; and no final RIA performed). BCCA and Phillips
commented that the proposed rule meets the definition of a major environmental
rule and that the RIA requirements of Texas Government Code, §2001.0225
are triggered because the proposed rule exceeds standards set by federal law
and exceeds an express requirement of state law. BCCA further commented that
the commission's efforts to avoid an RIA by asserting that the proposed rules
are exempt from the RIA requirements because federal law mandates the rules
is legally flawed and may render the rules invalid.
The commission disagrees with the commenters that the proposed rules meet
the definition of a major environmental rule and that its interpretation of
the exemption for federally mandated standards is legally flawed. While the
rules may require significant capital investments by inspection station owners,
the fee established under the rules should offset most, if not all of the
costs. Additionally, whether a rule is a "major environmental rule" alone
is not enough to trigger the RIA requirements. Texas Government Code, §2001.0225
only applies to a major environmental rule adopted by a state agency, the
result of which is to: 1) exceed a standard set by federal law, unless the
rule is specifically required by state law; 2) exceed an express requirement
of state law, unless the rule is specifically required by federal law; 3)
exceed a requirement of a delegation agreement or contract between the state
and an agency or representative of the federal government to implement a state
and federal program; or 4) adopt a rule solely under the general powers of
the agency instead of under a specific state law.
This rulemaking action does not meet any of these four applicability requirements,
and is adopted in substantial compliance with the RIA requirements. Texas
Government Code, §2001.035. These rules do not exceed an express standard
set by federal law because the I/M requirements are specifically developed
to meet the ozone NAAQS set by the EPA under 42 USC, §7409 and the requirement
for a severe nonattainment are to have an I/M program under 42 USC, §7511a(d).
Title 42 USC, §7410 requires states to adopt a SIP which provides for
"implementation, maintenance, and enforcement" of the primary NAAQS in each
air quality control region of the state. Failure to develop control strategies
to demonstrate attainment can result in federal sanctions. Specifically, as
noted elsewhere in this rule preamble, the emission reductions associated
with these rules are a necessary element of the attainment demonstration required
by the FCAA.
This conclusion is supported by the legislative history for Texas Government
Code, §2001.0225. During the 75th Legislative Session, SB 633 amended
the Texas Government Code to require agencies to perform an RIA of certain
rules. The intent of SB 633 was to require agencies to conduct a RIA of major
environmental rules that will have a material adverse impact, and will exceed
a requirement of state law, federal law, or a delegated federal program, or
are adopted solely under the general powers of the agency. The commission
provided a cost estimate for SB 633 that concluded "based on an assessment
of rules adopted by the agency in the past, it is not anticipated that the
bill will have significant fiscal implications for the agency due to its limited
application." The commission also noted that the number of rules that would
require assessment under the provisions of the bill was not large. Because
of the ongoing need to address nonattainment demonstrations required by federal
law, the commission routinely proposes and adopts SIP rules. If each rule
proposed for inclusion in the SIP was incorrectly considered as exceeding
federal law, every SIP rule would require the full RIA contemplated by SB
633. This result would be inconsistent with the cost estimates and fiscal
notes prepared by the commission and by the LBB. Since the legislature is
presumed to understand the fiscal impacts of the bills it passes, and that
presumption is based on information provided by state agencies and the LBB,
the commission believes that the intent of SB 633 was only to require the
full RIA for rules that meet the requirements under §2001.0225(a). While
the SIP rules will have a broad impact, that impact is no greater than is
necessary or appropriate to meet the requirements of the FCAA. In other words,
the proposed rules are intended to meet federal and state law, and do not
go above and beyond what is required to meet federal or state statutes.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
It is presumed that "when an agency interpretation is in effect at the time
the legislature amends the laws without making substantial change in the statute,
the legislature is deemed to have accepted the agency's interpretation."
The commission's interpretation of the RIA requirements is also supported
by a change made to the APA by the legislature in 1999. In an attempt to limit
the number of rule challenges based upon APA requirements, the legislature
clarified that state agencies are required to meet these sections of the APA
against the standard of "substantial compliance." Texas Government Code, §2001.035.
The legislature specifically identified Texas Government Code, §2001.0225
as falling under this standard. The commission has substantially complied
with the requirements of §2001.0225.
Therefore, in addition to not exceeding an express standard set by federal
law, these rules do not exceed state requirements, and are not adopted solely
under the general powers of the agency because the provisions of the TCAA, §§382.011,
382.012, 382.017, 382.019, 382.037 - 382.038, and 382.039 authorize the commission
to implement a plan for the control of the states air quality, including measures
necessary to meet federal requirements. The remaining applicability criteria,
pertaining to exceeding a delegation agreement or contract between the state
and the federal government does not apply. Thus, the commission is not required
to conduct a regulatory analysis as provided in Texas Government Code, §2001.0225.
BCCA, ExxonMobil, and Phillips commented that the rule was proposed without
an adequate takings impact assessment. The commenters stated that Section
2007 of the Texas Government Code requires an agency to prepare a written
takings impact assessment when proposing a rule. They further stated that
the assessment must describe the purpose of the proposed action; determine
whether engaging in the proposed action will constitute a taking; and describe
reasonable alternative actions that could accomplish the specified purpose
and explain whether these alternatives actions also would constitute takings.
BCCA and ExxonMobil stated that guidelines from the attorney general direct
an agency to carefully review governmental actions that have a significant
impact on the owner's economic interest. Finally, BCCA commented that commission
did not explain why the rule was reasonably taken to meet the federal requirement
and therefore does not qualify for the exemption claimed. BCCA stated that
this rule requires more than is necessary to meet the federal requirement.
The primary reason the commission determined that these rules did not constitute
a takings under Texas Government Code, Chapter 2007 is that they will not
burden private real property. These rules apply to motor vehicles and to equipment
required at vehicle inspection stations, neither of which are real property
or appurtenance thereto.
In its analysis, the commission also found that the rules are exempt from
Texas Government Code, Chapter 2007 pursuant to §2007.003(b)(4) because
they are reasonably taken to fulfill an obligation mandated by federal law.
The commission has included elsewhere in this preamble its reasoned justification
for adopting this strategy and has explained why it is a necessary component
of the SIP which is federally mandated. This discussion, as well as the HGA
SIP which is being adopted concurrently, explains in detail that every rule
in the HGA SIP package is necessary and that none of the reductions in those
packages represent more than is necessary to bring the area into attainment
with the NAAQS. Additionally, these rules implement an I/M program which is
specifically required by 42 USC, §7511a(d). This rulemaking therefore
meets the requirements of §2007.003(b)(4). Although the rule amendments
do not directly prevent a nuisance or prevent an immediate threat to life
or property, they do prevent a real and substantial threat to public health
and safety and significantly advance the health and safety purpose and therefore
meet the requirement of §2007.003(b)(13). For these reasons the rules
do not constitute a takings under Chapter 2007 and do not require additional
analysis.
BCCA, ExxonMobil, and Phillips66 commented that the small and micro-business
assessment was inadequate as provided. Specifically, the commenters stated
that the commission failed to consider the costs of compliance for small and
micro-businesses, and that the proposal did not adequately compare of the
cost of compliance for small businesses to the cost of compliance for the
largest businesses affected by the proposed rules. BCCA noted that none of
the Plan's small and micro-business assessments applied the mandated cost
comparison standards, even where the commission acknowledged "significant"
impact. BCCA commented that the commission either restated the costs of compliance
it identified in the analyses of public benefits and costs, or concluded that
it cannot determine the cost to small businesses. Finally, BCCA noted that
it is impossible for the public to provide comment on whether the commission
adequately considered the effect of the rule on small business because the
commission did not publish the information required by Texas law.
The agency has estimated, to the extent possible, the costs to small businesses
and has determined that the cost depends more upon either the number of motor
vehicles operated by the business or, for inspection stations, the number
of vehicle inspection lanes, and that it is not dependent upon the number
of employees, hours of labor, or amount of sales income. Some small businesses
have only one motor vehicle while others have large fleets. Large businesses
vary in the same way. The size of the fleet is not dependent upon the size
of the business. Additionally, for inspection stations, the number of lanes
dedicated to inspections will determine the amount of test equipment needed.
The commission has provided the estimated cost per vehicle and per piece of
testing equipment and argues that this is the only meaningful way to provide
sufficient notice of the cost to small business and therefore that it meets
the objective of Texas Government Code, Chapter 2006. This assertion is supported
by the fact that no small businesses provided comments which include cost
of compliance in terms of the number of employees, hours of labor, or amount
of sales income.
BCCA, ExxonMobil, and Phillips 66 stated that the proposed rules did not
include adequate notice as required under Texas Government Code, §2002.024.
The commenters stated that Texas Government Code, §2001.024, requires
adequate notice of a proposed rule, including information about its public
benefits and costs. The commenters stated that adequate notice is essential
for fairness as well as a meaningful opportunity to comment on a proposed
rule, and that courts have considered notice "adequate" only if: interested
persons can confront the agency's factual suppositions and policy preconceptions;
and the agency provides interested parties the opportunity to challenge the
underlying factual data relied upon by the agency. The commenters asserted
that in proposing the rules, the commission failed to provide interested parties
with sufficient information to constitute adequate notice.
BCCA stated that the rule proposal preamble appears short of adequate notice
because the cost estimates were "dramatically underestimated" and added that
the commission provided no bases for estimating that only 10% of the current
stations in Harris County would need to purchase new equipment.
The commenters stated that they had identified a number of critical gaps
in the underlying factual data, methodology, and analysis in support of the
proposed rules. The commenters asserted that the proposal included insufficient
information and analysis regarding costs and impacts. The commenters asserted
that the commission has not adequately responded to requests for additional
information from stakeholders. The commenters stated that the following requests
for information were outstanding: information regarding the modeling of emissions;
information regarding the corrected emissions inventory database; and information
supporting the estimated costs of control. The commenters stated that this
information is necessary in order to comment effectively on the proposed rules
and that data gaps in the proposal hindered effective comment.
The commission disagrees with the commenters and has made no change in
response to these comments. Texas Government Code, §2001.024 requires
of the notice of a proposed rule include certain information. Subsection (a)(5)
requires that the notice state the public benefits expected as a result of
the adoption of the proposed rule and the probable economic cost to persons
required to comply with the rule. Adequate notice is essential for fairness
as well as a meaningful opportunity to comment on a proposed rule.
United Loans, Inc. v. Pettijohn,
955 S.W.2d 649, 651 (Tex. App.-Austin
1997). To achieve the goal of encouraging meaningful public participation
in the formulation and adoption of rules by state agencies, the notice must
have sufficient information so that interested persons can determine whether
it is necessary for them to participate in order to protect their legal rights
and privileges. The proposed rules contained an analysis of information available
to the commission regarding the costs and benefits of the proposed rules.
The commission received intelligent comments which were substantial in both
number and in scope, regarding the costs as well as the benefits. Therefore,
the commission believes this goal has been achieved and that the notice includes
sufficient information to constitute adequate notice.
BCCA's statements that the costs were "dramatically underestimated" did
not state how that conclusion was reached. Mere disagreement with cost estimates
does not render notice inadequate. BCCA did not state that why they disagreed
with the commission's 10% estimate for stations in Harris County. In fact,
the commission based this estimate on knowledge of which machines are in use
under the current program and information from the vendor indicating whether
those machines can be upgrade or must be replaced altogether. To simply state
that the proposal failed to provide sufficient information does not provide
the commission with sufficient information to propose changes or alternative
strategies. The commenters did not say how the notice is insufficient, merely
that it is insufficient. Nevertheless, the commission has reviewed the notice
and has determined it is adequate.
Similarly, the comments which state there are critical gaps did not identify
what those gaps are or how that results in inadequate notice. The commission
is unaware of any requests for additional information to which it was not
completely responsive.
BCCA, ExxonMobil, and Phillips 66 stated that the proposed rules did not
include the local employment impact statement required under Texas Government
Code, §2001.022. The commenters stated that Texas Government Code, §2001.022,
requires the commission to determine whether the rule proposal has the potential
to affect a local economy before proposing the rule for adoption. The commenters
stated that if answered affirmatively, the commission must request the Texas
Employment Commission prepare a local employment impact statement describing
in detail the probable effect of the rule on employment in each geographic
area affected by the rule for each year of the first five years that the rule
will be in effect. The commenters further asserted that the commission failed
to make the required initial determination and ignored the potential for the
proposal to adversely affect the local economy. The commenters stated that
a local employment impact statement should have been requested and prepared
in advance of the proposal.
The commission agrees with the commenters that the proposed rules may affect
a local economy, however, does not agree that it is the responsibility of
the commission to provide the local employment impact analysis. The APA requires
state agencies to determine whether a rule may affect a local economy before
proposing a rule for adoption. If the agency determines that a proposed rule
may affect a local economy, the agency must send a copy of the proposed rule
and other information to the Texas Workforce Commission (Workforce Commission)
before the agency files notice of the proposed rule with the secretary of
state. The APA requires the Workforce Commission to prepare a local employment
impact statement for proposed rules, if a state agency requests the statement.
The commission determined that the proposed rules might affect a local economy,
and sent the proposed rules and other requested information to the Workforce
Commission. The commission received a letter from the Workforce Commission,
indicating that the Workforce Commission did not have the ability to determine
the potential local employment impacts from the proposed rules.
STATUTORY AUTHORITY
The amendments are adopted under Texas Water Code (TWC), §5.103, which
provides the commission the authority to adopt rules necessary to carry out
its powers and duties under the TWC. The amendments are also adopted under
the Texas Health and Safety Code, TCAA, §382.011, which provides the
commission the authority to control the quality of the state's air; §382.012,
which provides the commission the authority to prepare and develop a general,
comprehensive plan for the control of the state's air; §382.017, which
provides the commission the authority to adopt rules consistent with the 0policy
and purposes of the TCAA; §382.019, which provides the commission the
authority to adopt rules to control and reduce emissions from engines used
to propel land vehicles; §382.037 through §382.038, which provide
the commission the authority by rule to establish, implement, and administer
a program requiring emissions-related inspections of motor vehicles to be
performed at inspection facilities consistent with the requirements of the
FCAA; and §382.039, which provides the commission the authority to coordinate
with federal, state, and local transportation planning agencies to develop
and implement transportation programs and other measures necessary to demonstrate
and maintain attainment of NAAQS and to protect the public from exposure to
hazardous air contaminants from motor vehicles.
§114.50.Vehicle Emissions Inspection Requirements.
(a)
Applicability. The requirements of this section and those
contained in the revised Texas Inspection and Maintenance (I/M) State Implementation
Plan (SIP) shall be applied to all gasoline-powered motor vehicles 2-24 years
old and subject to an annual emissions inspection, beginning with the first
safety inspection. Currently, military tactical vehicles, motorcycles, diesel-powered
vehicles, dual-fueled vehicles which cannot operate using gasoline, and antique
vehicles registered with the Texas Department of Transportaiton are excluded
from the program. Safety inspection facilities and inspectors certified by
the Texas Department of Public Safety (DPS) shall inspect all subject vehicles,
in the following program areas in accordance with the following schedule.
(1)
All vehicles registered and primarily operated in Dallas,
Tarrant, Harris, and El Paso Counties shall be tested using a two-speed idle
(TSI) test through April 30, 2002.
(2)
This paragraph applies to all vehicles registered and primarily
operated in the Dallas/Fort Worth (DFW) program area.
(A)
Beginning May 1, 2002, all 1996 and newer model year vehicles
registered and primarily operated in Collin, Dallas, Denton, and Tarrant Counties
equipped with on-board diagnostic (OBD) systems shall be tested using EPA-approved
OBD test procedures. If OBD data cannot be collected from the vehicle, an
EPA-approved tail-pipe emissions test will be used.
(B)
Beginning May 1, 2002, all pre-1996 model year vehicles
registered and primarily operated in Collin, Dallas, Denton, and Tarrant Counties
shall be tested using an acceleration simulation mode (ASM-2) test, or a
vehicle emissions test that meets SIP emissions reduction requirements and
is approved by the EPA.
(3)
This paragraph applies to all vehicles registered and primarily
operated in the extended DFW (EDFW) program area.
(A)
Beginning May 1, 2003, all 1996 and newer model year vehicles
registered and primarily operated in Ellis, Johnson, Kaufman, Parker, and
Rockwall Counties equipped with OBD systems shall be tested using EPA-approved
OBD test procedures. If OBD data cannot be collected from the vehicle, an
EPA approved tail-pipe emissions test will be used.
(B)
Beginning May 1, 2003, all pre-1996 and older model year
vehicles registered and primarily operated in Ellis, Johnson, Kaufman, Parker,
and Rockwall Counties shall be tested using an ASM-2 test, or a vehicle emissions
test that meets SIP emissions reduction requirements and is approved by the
EPA.
(4)
This paragraph applies to all vehicles registered and primarily
operated in the Houston/Galveston (HGA) program area.
(A)
Beginning May 1, 2002, all 1996 and newer model year vehicles
registered and primarily operated in Harris County equipped with OBD systems
shall be tested using EPA-approved OBD test procedures. If OBD data cannot
be collected from the vehicle, an EPA approved tail-pipe emissions test will
be used.
(B)
Beginning May 1, 2002, all pre-1996 model year vehicles
registered and primarily operated in Harris County shall be tested using an
ASM-2 test, or a vehicle emissions test that meets SIP emissions reduction
requirements and is approved by the EPA.
(C)
Beginning May 1, 2003, all 1996 and newer model year vehicles
equipped with OBD systems and registered and primarily operated in Brazoria,
Fort Bend, Galveston, and Montgomery Counties shall be tested using EPA-approved
OBD test procedures. If OBD data cannot be collected from the vehicle, an
EPA approved tail-pipe emissions test will be used.
(D)
Beginning May 1, 2003, all pre-1996 and newer model year
vehicles registered and primarily operated in Brazoria, Fort Bend, Galveston,
and Montgomery Counties shall be tested using the ASM-2 test procedures, or
a vehicle emissions test that meets SIP emissions reduction requirements and
is approved by the EPA.
(E)
Beginning May 1, 2004, all 1996 and newer model year vehicles
equipped with OBD systems and registered and primarily operated in Chambers,
Liberty, and Waller Counties shall be tested using EPA-approved OBD test procedures.
If OBD data cannot be collected from the vehicle, an EPA-approved tail-pipe
emissions test will be used.
(F)
Beginning May 1, 2004, all pre-1996 model year vehicles
registered and primarily operated in Chambers, Liberty, and Waller Counties
shall be tested using an ASM-2 test, or a vehicle emissions test that meets
SIP emissions reduction requirements and is approved by the EPA.
(G)
If Chambers, Liberty, and Waller Counties and their respective
largest municipality submit by May 1, 2002, individually or collectively,
a resolution that is approved by the commission and EPA as an alternative
air control plan, then subparagraphs (E) - (F) of this paragraph are not required.
The resolution should provide a control plan that will provide modeled reductions
of volatile organic compounds and nitrogen oxides equivalent to the reductions
that have been modeled for these counties through the implementation of the
I/M program. In determining approvability of a plan, the commission will consider
federal I/M program requirements.
(5)
This paragraph applies to all vehicles registered and primarily
operated in the El Paso program area.
(A)
Beginning May 1, 2002, all 1996 and newer model year vehicles
equipped with OBD systems shall be tested using EPA-approved OBD test procedures.
If OBD data cannot be collected from the vehicle, an EPA-approved tail-pipe
emissions test will be used.
(B)
Beginning May 1, 2002, all pre-1996 vehicles shall be tested
using a TSI test.
(b)
Control requirements.
(1)
No person or entity may operate, or allow the operation
of, a motor vehicle registered in the DFW, EDFW, HGA, and El Paso program
areas which does not comply with:
(A)
all applicable air pollution emissions control related
requirements included in the annual vehicle safety inspection requirements
administered by DPS, as evidenced by a current valid inspection certificate
affixed to the vehicle windshield; and
(B)
the vehicle emissions inspection and maintenance requirements
contained in this subchapter.
(2)
All federal government agencies shall require a motor vehicle
operated by any federal government agency employee on any property or facility
under the jurisdiction of the agency and located in a program area to comply
with all vehicle emissions I/M requirements contained in the revised Texas
I/M SIP. Commanding officers or directors of federal facilities shall certify
annually to the executive director, or appointed designee, that all subject
vehicles have been tested and are in compliance with the Federal Clean Air
Act (42 United States Code, et seq.). This requirement shall not apply to
visiting agency, employee, or military personnel vehicles as long as such
visits do not exceed 60 calendar days per year.
(3)
Any motorist in the DFW, EDFW, HGA, or El Paso program
areas who has received a notice from an emissions inspection station that
there are recall items unresolved on their motor vehicle, should furnish proof
of compliance with the recall notice prior to the next vehicle emissions inspection.
The motorist may present a written statement from the dealership or leasing
agency indicating that emissions repairs have been completed as proof of compliance.
(4)
A motorist whose vehicle has failed an emissions test may
request a challenge retest through DPS. If the retest is conducted within
15 days of the initial inspection, the retest is free.
(5)
A motorist whose vehicle has failed an emissions test and
has not requested a challenge retest or has failed a challenge retest must
have emissions-related repairs performed and must submit a properly completed
Vehicle Repair Form (VRF) in order to receive a retest, a minimum expenditure
waiver, or a parts availability time extension.
(6)
A motorist whose vehicle is registered in the DFW, EDFW,
HGA, or El Paso program areas and has failed an on-road test administered
by the DPS shall:
(A)
submit the vehicle for an out-of-cycle vehicle emissions
inspection within 30 days of written notice by the DPS; and
(B)
satisfy all inspection, extension, or waiver requirements
of the vehicle emissions I/M program contained in the revised Texas I/M SIP.
(7)
State, governmental, and quasi-governmental agencies which
fall outside the normal registration or inspection process shall comply with
all vehicle emissions I/M requirements contained in the Texas I/M SIP for
vehicles primarily operated in I/M program areas.
(c)
Waivers and extensions. A motorist may apply to the DPS
for a waiver or an extension as specified in §114.52 of this title (relating
to Waivers and Extensions for Inspection Requirements), which defer the need
for full compliance with vehicle emissions standards for a specified period
of time after failing a vehicle emissions inspection.
(d)
Prohibitions.
(1)
No person may issue or allow the issuance of a vehicle
inspection report (VIR), as authorized by DPS, unless all applicable air pollution
emissions control related requirements of the annual vehicle safety inspection
and the vehicle emissions I/M requirements and procedures contained in the
revised Texas I/M SIP are completely and properly performed in accordance
with the rules and regulations adopted by DPS and the commission. Prior to
taking any enforcement action regarding this provision, the commission shall
consult with DPS.
(2)
No person may allow or participate in the preparation,
duplication, sale, distribution, or use of false, counterfeit, or stolen safety
inspection certificates, VIRs, VRFs, vehicle emissions repair documentation,
or other documents which may be used to circumvent the vehicle emissions I/M
requirements and procedures contained in the revised Texas I/M SIP.
(3)
No organization, business, person, or other entity may
represent itself as an emissions inspector certified by the DPS, unless such
certification has been issued under the certification requirements and procedures
contained in the Texas Transportation Code, §§548.401 - 548.404.
(4)
No person may act as or offer to perform services as a
Recognized Emissions Repair Technician of Texas, (as designated by DPS), without
first obtaining and maintaining DPS recognition.
§114.52.Waivers and Extensions for Inspection Requirements.
(a)
Applicability. The waivers and extensions apply to any
motorist who can satisfy the conditions of a specific waiver or extension.
Applications must be made to the Department of Public Safety (DPS). For the
minimum expenditure waiver, individual vehicle waiver, and parts availability
time extension, the motorist may apply only once during each testing cycle.
For the low income time extension, the motorist may apply every other test
cycle.
(b)
Minimum expenditure waiver. A motorist shall use any available
warranty coverage to obtain needed repairs before expenditures shall be used
in calculating the minimum repair expenditures to qualify for a minimum expenditure
waiver, unless the warranty remedy has been denied in writing from the manufacturer
or authorized dealer. A motorist may not use or attempt to use expenditures
for tampering-related repairs in calculating the minimum repair expenditures
to qualify for a minimum expenditure waiver. A minimum expenditure waiver
shall be valid for the remaining portion of the testing cycle. Tampering includes,
but is not limited to, engine modifications, emissions system modifications,
or fuel-type modifications disapproved by the Texas Natural Resource Conservation
Commission or EPA. A minimum expenditure waiver may be granted in accordance
with the following conditions:
(1)
The applicant must have a valid retest Vehicle Inspection
Report (VIR), a valid Vehicle Repair Form (VRF), and the vehicle must have
failed a retest after all qualifying repairs. Qualifying repairs must meet
the following conditions.
(A)
The minimum expenditure waiver in any program area shall
be at least $450 or that amount adjusted by the Consumer Price Index.
(B)
All qualifying repairs shall be performed by a Recognized
Emissions Repair Technician of Texas (as designated by DPS) in order to count
labor cost and/or diagnostic costs.
(C)
Qualifying repairs must be directly applicable to the cause
for the test failure (repairs conducted up to 60 days prior to the initial
test may count toward the waiver amount).
(D)
When repairs are not performed by a Recognized Emissions
Repair Technician of Texas, only the purchase price of parts, applicable to
the failure, qualify as a repair expenditure for the minimum expenditure waiver.
(2)
The motorist provides to the DPS an original retest VIR,
a properly completed VRF, and an original itemized receipt indicating the
emissions-related repairs performed. If labor and/or diagnostic charges are
being claimed toward the minimum expenditure, the VRF shall be completed by
a Recognized Emissions Repair Technician of Texas.
(c)
Low income time extension. A low income time extension
may be granted in accordance with the following conditions.
(1)
A motorist must supply proof that the subject vehicle failed
the initial emissions inspection test in the form of an original failed vehicle
inspection report.
(2)
A motorist shall provide proof in writing to the DPS that
the registered vehicle owner(s) meet(s) the following conditions:
(A)
the low income time extension applicant is the owner of
the vehicle that has failed an inspection and maintenance (I/M) test;
(B)
the vehicle has not been granted a low income time extension
waiver in the previous inspection cycle; and
(C)
the applicant meets one of the following:
(i)
the applicant receives financial assistance from the Texas
Department of Human Services (subject to approval by the director of DPS);
or
(ii)
the applicant's adjusted gross income is within the current
federal poverty income guidelines;
(D)
the applicant shows proof of conformity with paragraph
(2)(C) of this subsection by providing to the DPS one of the following, which
the applicant certifies are true and correct:
(i)
a federal income tax return; or
(ii)
other documentation authorized by the director of the
DPS.
(3)
After a motorist receives an initial low income time extension,
the vehicle must pass an emissions test prior to receiving another low income
time extension or any waiver or extension.
(d)
Parts availability time extension. The parts availability
time extension does not exempt the vehicle from the compliance requirements
of the I/M program but merely extends the period for compliance. By the end
of the time extended, the vehicle must be repaired, retested, and receive
a passing VIR or comply with paragraph (4) of this subsection. Only one parts
availability time extension is allowed in each test cycle for each vehicle.
A parts availability time extension may be granted in accordance with the
following conditions.
(1)
The motorist can document that emissions-related repairs
cannot be completed before the expiration of the safety inspection certificate
or before the 30-day period following an out-of-cycle inspection because the
repairs require an uncommon part.
(2)
The motorist shall provide to the DPS an original VIR indicating
that the vehicle failed the emissions test and an original itemized documentation
by a Recognized Emissions Repair Technician of Texas, indicating parts ordered
by name; description and catalog number; order number; sources of parts, including
addresses and phone numbers; and expected delivery and installation dates
of uncommon parts before a parts availability time extension can be issued.
(3)
The motorist shall return the motor vehicle to the DPS
for a retest and verification of repairs upon completion of the repairs.
(4)
The motorist shall provide to the DPS, prior to expiration
of a parts availability time extension, adequate documentation that one of
the following conditions exists:
(A)
the motor vehicle passed a retest;
(B)
the motorist qualifies for a Minimum Expenditure Waiver
or Low Income Time Extension; or
(C)
the motor vehicle shall no longer be operated in the program
area.
(5)
A vehicle which receives a parts availability time extension
in one test cycle must have the vehicle repaired and retested prior to the
expiration of such extension or the vehicle shall be ineligible for a parts
availability time extension in the subsequent test cycle in addition to other
penalties authorized for non-compliance.
(6)
The length of a parts availability time extension shall
depend upon expected delivery and installation dates of uncommon parts as
determined by the DPS representative on a case-by-case basis and issued for
either 30, 60, or 90 days or longer if necessary, but shall not exceed one
test cycle.
(e)
Individual vehicle waiver. If a vehicle has failed an I/M
test, a motorist may petition the director of the DPS for an individual vehicle
waiver. Upon demonstration that the motorist has taken reasonable measures
to comply with the requirements of the vehicle emissions I/M program contained
in the revised Texas I/M State Implementation Plan and that such waiver shall
have minimal impact on air quality, the director may approve the petition,
and the motorist may receive a waiver. Motorists may apply for the individual
vehicle waiver each test cycle.
§114.53.Inspection and Maintenance Fees.
(a)
The following fees must be paid for an emissions inspection
of a vehicle at an inspection station. This fee shall include one free retest
should the vehicle fail the emissions inspection, provided that the motorist
has the retest performed at the same station where the vehicle originally
failed and submits, prior to the retest, a properly completed Vehicle Repair
Form showing that emissions-related repairs were performed and the retest
is conducted within 15 days of the initial emissions test.
(1)
Through April 30, 2002, any emissions inspection station
required to conduct a two-speed idle (TSI) test in accordance with §114.50(a)(1)
of this title (relating to Vehicle Emissions Inspection Requirements) shall
collect a fee of $13 and shall remit $1.75 to the Department of Public Safety
(DPS).
(2)
In El Paso County beginning May 1, 2002, any emissions
inspection station required to conduct an emissions test in accordance with §114.50(a)(5)(A)
or (B) of this title (relating to Vehicle Emissions Inspection Requirements)
shall collect a fee of $14.
(3)
In the Dallas/Fort Worth (DFW) program area beginning May
1, 2002, any emissions inspection station required to conduct an emissions
test in accordance with §114.50(a)(2)(A) or (B), and in the extended
DFW (EDFW) program area beginning May 1, 2003, any emissions inspection station
required to conduct an emissions test in accordance with §114.50(a)(3)(A)
or (B) of this title shall collect a fee of $22.50.
(4)
In the Houston/Galveston program area beginning May 1,
2002, any emissions inspection station in Harris County required to conduct
an emissions test in accordance with §114.50(a)(4)(A) or (B); beginning
May 1, 2003, any emissions inspection station in Brazoria, Fort Bend, Galveston,
and Montgomery Counties required to conduct an emissions test in accordance
with §114.50(a)(4)(C) or (D); and beginning May 1, 2004, any emissions
inspection station in Chambers, Liberty, and Waller Counties required to conduct
an emissions test in accordance with §114.50(a)(4)(E) or (F) shall collect
a fee of $22.50.
(b)
The per-vehicle fee and the amount the inspection station
remits to the DPS for a challenge test, at an inspection station designated
by the DPS, shall be the same as the amounts set forth in subsection (a) of
this section. The challenge fee shall not be charged if the vehicle is retested
within 15 days of the initial test.
(c)
Inspection stations performing out-of-cycle vehicle emissions
inspections for the state's remote sensing element shall charge a motorist
for an out-of-cycle emissions inspection in the amount specified in subsection
(a) of this section, resulting from written notification that subject vehicle
failed on-road testing. If the vehicle passes the vehicle emissions inspection,
the vehicle owner may request reimbursement from DPS.
This agency hereby certifies that the adoption has been reviewed
by legal counsel and found to be a valid exercise of the agency's legal authority.
Filed with the Office of
the Secretary of State on December 29, 2000.
TRD-200009077
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Effective date: January 18, 2001
Proposal publication date: August 25, 2000
For further information, please call: (512) 239-0348
3.
NON-ROAD LARGE SPARK-IGNITION ENGINES
30 TAC §114.421, §114.429
The Texas Natural Resource Conservation Commission (commission)
adopts amendments to §114.421, Emission Specifications, and §114.429,
Affected Counties and Compliance Schedules. These amendments to Chapter 114,
Control of Air Pollution from Motor Vehicles; Subchapter I, Non-road Engines;
Division 3, Non-road Large Spark-ignition Engines; and corresponding revisions
to the associated state implementation plan (SIP) are being adopted in order
to extend the existing requirements for non-road, large spark-ignition (LSI)
engines to all counties in the state thus controlling ground-level ozone in
the state. These amendments are one element of the control strategy for the
HGA Post-1999 Rate-of-Progress (ROP)/Attainment Demonstration SIP. The new §114.421
and §114.429 are adopted
without changes
to the proposed text as published in the August 25, 2000 issue of the
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE ADOPTED RULE
The Houston/Galveston (HGA) ozone nonattainment area is classified as Severe-17
under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States
Code (USC), §§7401 et seq.), and therefore is required to attain
the one-hour ozone standard of 0.12 parts per million (ppm) by November 15,
2007. In addition, 42 USC, §7502(a)(2), requires attainment as expeditiously
as practicable, and 42 USC, §7511a(d), requires states to submit ozone
attainment demonstration SIPs for severe ozone nonattainment areas such as
HGA. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris,
Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration
of attainment in accordance with 42 USC, §7410. On January 4, 1995, the
state submitted the first of its Post-1996 SIP revisions for HGA.
The January 1995 SIP consisted of urban airshed model (UAM) modeling for
1988 and 1990 base-case episodes, adopted rules to achieve a 9% ROP reduction
in volatile organic compounds (VOC), and a commitment schedule for the remaining
ROP and attainment demonstration elements. At the same time, but in a separate
action, the State of Texas filed for the temporary nitrogen oxides (NO
Around the same time as the 1995 submittal, the EPA policy regarding SIP
elements and timelines went through changes. Two national programs in particular
resulted in changing deadlines and requirements. The first of these programs
was the Ozone Transport Assessment Group (OTAG). This group grew out of a
March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for
Air and Radiation, that allowed states to postpone completion of their attainment
demonstrations until an assessment of the role of transported ozone and precursors
had been completed for the eastern half of the nation, including the eastern
portion of Texas. Texas participated in this study, and it has been concluded
that Texas does not significantly contribute to ozone exceedances in the Northeastern
United States. The other major national initiative that has impacted the SIP
planning process is the revisions to the national ambient air quality standard
(NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing
the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996,
concurrent with the proposal of the standards, the EPA proposed an interim
implementation plan (IIP) that it believed would help areas like HGA transition
from the old to the new standard. In an attempt to avoid a significant delay
in planning activities, Texas began to follow this guidance, and readjusted
its modeling and SIP development timelines accordingly. When the new standard
was published, the EPA decided not to publish the IIP, and instead stated
that, for areas currently exceeding the one-hour ozone standard, that standard
would continue to apply until it is attained. The FCAA requires that HGA attain
the standard by November 15, 2007.
The EPA issued revised draft guidance for areas such as HGA that do not
attain the one-hour ozone standard. The commission adopted on May 6, 1998
and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained
the following elements in response to the EPA guidance: UAM modeling based
on emissions projected from a 1993 baseline out to the 2007 attainment date;
an estimate of the level of VOC and NO
x
reductions
necessary to achieve the one-hour ozone standard by 2007; a list of control
strategies that the state could implement to attain the one-hour ozone standard;
a schedule for completing the other required elements of the attainment demonstration;
a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the
EPA believed made the previous version of that SIP unapprovable; and evidence
that all measures and regulations required by the Subpart 2 of Title I of
the FCAA to control ozone and its precursors have been adopted and implemented,
or are on an expeditious schedule to be adopted and implemented.
In November 1998, the SIP revision submitted to the EPA in May 1998 became
complete by operation of law. However, the EPA stated that it could not approve
the SIP until specific control strategies were modeled in the attainment demonstration.
The EPA specified a submittal date of November 15, 1999 for this modeling.
In a letter to the EPA dated January 5, 1999, the state committed to model
two strategies showing attainment.
As the HGA modeling protocol evolved, the state eventually selected and
modeled seven basic modeling scenarios. As part of this process, a group of
HGA stakeholders worked closely with commission staff to identify local control
strategies for the modeling. Some of the scenarios for which the stakeholders
requested evaluation included options such as California-type fuel and vehicle
programs as well as an acceleration simulation mode equivalent motor vehicle
inspection and maintenance program. Other scenarios incorporated the estimated
reductions in emissions that were expected to be achieved throughout the modeling
domain as a result of the implementation of several voluntary and mandatory
statewide programs adopted or planned independently of the SIP. It should
be made clear that the commission did not propose that any of these strategies
be included in the ultimate control strategy submitted to the EPA in 2000.
The need for and effectiveness of any controls which may be implemented outside
the HGA eight-county area will be evaluated on a county-by-county basis.
The SIP revision was adopted by the commission on October 27, 1999, submitted
to the EPA by November 15, 1999, and contained the following elements: photochemical
modeling of potential specific control strategies for attainment of the one-hour
ozone standard in the HGA area by the attainment date of November 15, 2007;
an analysis of seven specific modeling scenarios reflecting various combinations
of federal, state, and local controls in HGA (additional scenarios H1 and
H2 build upon Scenario VIf); identification of the level of reductions of
VOC and NO
x
necessary to attain the one-hour
ozone standard by 2007; a 2007 mobile source budget for transportation conformity;
identification of specific source categories which, if controlled, could result
in sufficient VOC and/or NO
x
reductions to attain
the standard; a schedule committing to submit by April 2000 an enforceable
commitment to conduct a mid-course review; and a schedule committing to submit
modeling and adopted rules in support of the attainment demonstration by December
2000.
The April 19, 2000 SIP revision for HGA contained the following enforceable
commitments by the state: to quantify the shortfall of NO
x
reductions needed for attainment; to list and quantify potential
control measures to meet the shortfall of NO
x
reductions needed for attainment; to adopt the majority of the necessary rules
for the HGA attainment demonstration by December 31, 2000, and to adopt the
rest of the shortfall rules as expeditiously as practical, but no later than
July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform
a mid-course review by May 1, 2004; and to perform modeling of mobile source
emissions using the EPA mobile source emissions model (MOBILE6), to revise
the on-road mobile source budget as needed, and to submit the revised budget
within 24 months of the model's release. In addition, if a conformity analysis
is to be performed between 12 months and 24 months after the MOBILE6 release,
the state will revise the motor vehicle emissions budget (MVEB) so that the
conformity analysis and the SIP MVEB are calculated on the same basis.
In order for the state to have an approvable attainment demonstration,
the EPA indicated that the state must adopt those strategies modeled in the
November submittal and then adopt sufficient controls to close the remaining
gap in NO
x
emissions. The modeling and other
analysis supporting these rules and the HGA SIP indicate a gap of approximately
an additional 91 tons per day (tpd) of NO
x
reductions
is necessary for an approvable attainment demonstration. The commission estimates
that this measure will achieve a minimum of 2.8 tpd of NO
x
equivalent reductions and is therefore a necessary measure to consider
for closing the gap and successfully demonstrating attainment.
The emission reduction requirements included as part of this SIP revision
represent substantial, intensive efforts on the part of stakeholder coalitions
in the HGA area. These coalitions, involving local governmental entities,
elected officials, environmental groups, industry, consultants, and the public,
as well as the commission and the EPA, have worked diligently to identify
and quantify potential control strategy measures for the HGA attainment demonstration.
Local officials from the HGA area formally submitted a resolution to the commission,
requesting the inclusion of many specific emission reduction strategies.
This rule adoption is one element of the control strategy for the HGA SIP.
Adoption and implementation of this control strategy is necessary in order
for the HGA nonattainment area to comply with the requirements of the FCAA
and achieve attainment for ozone. Additional elements of the control strategy
for the HGA SIP are being adopted concurrently in this issue of the
The amount of NO
x
reductions required for
the area to attain the ozone NAAQS has been estimated by extensive use of
sophisticated air quality grid modeling, which because of its scientific and
statutory grounding, is the chief policy tool for designing emission reduction
strategies. The FCAA, 42 USC, §7511a(c)(2), requires the use of photochemical
grid modeling for ozone nonattainment areas designated serious, severe, or
extreme. The modeling has been conducted with input from a technical oversight
committee. Commission staff have continued to improve the air quality modeling
technology and refine emission inventory data. Numerous emission control strategies
were considered in developing the modeling. Varying degrees of reductions
from point sources, on-road and non-road mobile sources, and area sources
were analyzed in multiple iterations of modeling, to test the effectiveness
of different NO
x
reductions. The attainment demonstration
modeling and other analysis submitted for public hearing and comment concurrently
with the HGA SIP show that a significant amount of NO
x
reductions practicably achievable are necessary from ozone control
strategies in order for the HGA nonattainment area to achieve the ozone NAAQS
by 2007, including reductions from surrounding counties included in the HGA
consolidated metropolitan statistical area (CMSA).
Additionally, reductions associated from the ozone control strategies that
will be implemented outside the HGA nonattainment area will benefit the HGA
nonattainment area. This is due to the regional nature of air pollution, the
contribution from mobile sources, and the economies of scale and associated
market advantages related to distribution networks for some strategies. At
the time the 1990 FCAA Amendments were enacted, the focus on controlling ozone
pollution was centered on local controls. However, for many years an ever
increasing number of air quality professionals have concluded that ozone is
a regional problem requiring regional strategies in addition to local control
programs. As nonattainment areas across the United States prepared attainment
demonstration SIPs in response to the 1990 FCAA Amendments, several areas
found that modeling attainment was made much more difficult, if not impossible,
due to high ozone and ozone precursor levels entering from the boundaries
of their respective modeling domains, commonly called transport. Recent science
indicates that regional approaches may provide improved control of ozone air
pollution.
The current SIP revision contains rules, enforceable commitments, photochemical
modeling analyses, and calculation of the remaining NO
x
reductions required to reach attainment (gap calculation) in support
of the HGA ozone attainment demonstration. In addition, this SIP contains
Post-1999 ROP plans for the milestone years 2002 and 2005, and for the attainment
year 2007. The SIP also contains enforceable commitments to implement further
measures, if needed, in support of the HGA attainment demonstration, as well
as a commitment to perform and submit a mid-course review.
The HGA ozone nonattainment area will need to ultimately reduce NO
The EPA has been regulating highway (on-road) cars and trucks since the
early 1970s and continues to set increasingly stringent emissions standards
for such vehicles. After considerable progress was made in controlling emissions
from on-road vehicles, the EPA turned its attention to non-road (also called
off-road) engines, which also contribute significantly to air pollution. Although
emissions from non-road, LSI engines have not yet been regulated by the EPA,
the California Air Resources Board (CARB) has adopted exhaust emission standards
for these engines. Non-road, LSI engines are primarily used to power industrial
equipment such as forklifts, generators, pumps, compressors, aerial lifts,
sweepers, and large lawn tractors. The engines are similar to automotive engines
and can use similar automotive technology, such as closed-loop engine control
and three-way catalysts, to reduce emissions.
The CARB determined the exhaust emission standards for non-road, LSI engines
to be technologically feasible and a cost-effective strategy at $.25 per pound
($500 per ton) of NO
x
and hydrocarbons (HC) reduced,
that will move the state toward reducing NO
x
and HC from non-road, LSI engines. HC, also called VOC, and NO
x
are precursor chemicals that contribute to the formation of ground-level
ozone. The HGA area alone will contain 23% of the state's LSI engines, or
approximately 88,374 engines, by 2007. Statewide, there will be approximately
371,096 LSI engines by 2007. Adoption and implementation of California standards
for non-road, LSI engines throughout the state should reduce the amount of
VOC and NO
x
emissions from these sources and,
therefore, help control ground-level ozone in nonattainment areas. For the
HGA ozone nonattainment area, emission reductions by 2007 will be approximately
2.8 tpd. The program is estimated to cost about $500 per ton of NO
x
reduced, which compares very favorably with the cost per ton of other
emission control strategies.
These amendments are adopted in order to control ground-level ozone in
the state by requiring model year 2004 and subsequent non-road, LSI engines
25 horsepower (hp) and larger to be certified under Title 13, California Code
of Regulations, Chapter 9, concerning Off-Road Vehicles and Engines Pollution
Control Devices (13 CCR 9), as adopted by the CARB on October 19, 1999 and
effective November 18, 1999. The commission is incorporating the non-road,
LSI engine rules by reference due to the need for the Texas program to remain
identical to the program in California. For any state program that differs
from the federal standards, 42 USC, §7543(e)(2)(B), requires the state
programs to be identical. The rules will be effective throughout the State
of Texas. These amendments are necessary in order to attain and maintain the
ozone standard in nonattainment areas, and to establish a single equipment
design standard for the state. A single equipment design standard will help
to prevent incompatibility and expense which may arise from the distribution
of equipment with different emission standards.
The commission solicited comment on additional flexibilities relating to
rule content and implementation which have not been addressed in this or other
concurrent rulemakings. These flexibilities may be available for both mobile
and stationary sources. Additional flexibilities may also be achieved through
innovative and/or emerging technology which may become available in the future.
Additional sources of funds for incentive programs may become available to
substitute for some of the measures considered here. There were 46 comments
received which are addressed in the ANALYSIS OF TESTIMONY section of this
preamble.
SECTION BY SECTION DISCUSSION
The intent of these amendments is to extend to all counties in the State
of Texas the non-road, LSI standards that currently exist in the Dallas/Fort
Worth (DFW) area. These existing standards are identical to the non-road,
LSI standards in place in California.
The following sections of Division 3 were adopted during the DFW rule promulgation
and were not reopened for public comment in this rulemaking action because
no changes were proposed to these sections: §114.420, Definitions; §114.422,
Control Requirements; and §114.427, Exemptions. The two sections of the
rules being opened for comment were §114.421 and §114.429. Section
114.421 is amended to reflect the state-wide applicability of the LSI rules,
and §114.429 is amended to reflect the compliance dates for the new portions
of the state being affected by this rulemaking action.
Additionally, §§114.420, 114.422, and 114.427 were not reopened
because they incorporate by reference the California non-road, LSI rules as
those rules are set out in 13 CCR 9, concerning Off-Road Vehicles and Engines
Pollution Control Devices, as adopted by the CARB on October 19, 1999 and
effective November 18, 1999. The Texas program must remain identical to the
California program, so the sections already incorporated by reference in the
DFW rulemaking may not be changed to be different from the California 13 CCR
9 rules.
Existing §114.421 (Emission Specifications) incorporated by reference
the 42 definitions found in 13 CCR 9, §2431 (Definitions). This rulemaking
action made no changes to these definitions. Existing §114.429 applied
the control requirements to nine counties in the DFW area which include Collin,
Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, and Tarrant Counties.
These amendments extend the control requirements to all counties within the
state. Section 114.429 also specifies the compliance schedule for engine manufacturers.
FINAL REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the rulemaking action in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225, and determined
that the rulemaking action does not meet the definition of a "major environmental
rule" as defined in that statute. "Major environmental rule" means a rule,
the specific intent of which is to protect the environment or reduce risks
to human health from environmental exposure and that may adversely affect
in a material way the economy, a sector of the economy, productivity, competition,
jobs, the environment, or the public health and safety of the state or a sector
of the state.
These adopted rules do not meet any of the four applicability criteria
for requiring a regulatory analysis of "major environmental rule" as defined
in the Texas Government Code. Section 2001.0225 applies only to a major environmental
rule the result of which is to: 1) exceed a standard set by federal law, unless
the rule is specifically required by state law; 2) exceed an express requirement
of state law, unless the rule is specifically required by federal law; 3)
exceed a requirement of a delegation agreement or contract between the state
and an agency or representative of the federal government to implement a state
and federal program; or 4) adopt a rule solely under the general powers of
the agency instead of under a specific state law.
The new sections to Chapter 114 are one element of the HGA attainment SIP.
While the amended rules are intended to protect the environment, based on
the analysis provided in the preamble, including the discussion in the PUBLIC
BENEFIT AND COSTS section of the proposal preamble, the commission does not
believe the rules will adversely affect, in a material way, the sale or use
of non-road, LSI engines. The commission does not believe these entities comprise
a sector of the economy, or that these rules will adversely affect in a material
way the economy, productivity, competition, jobs, the environment, or the
public health and safety of the state or a sector of the state.
These amendments to Chapter 114 are intended to protect the environment
or reduce risks to human health from environmental exposure to ozone but are
not anticipated to affect in a material way, the economy, a sector of the
economy, productivity, competition, jobs, the environment, or the public health
and safety of the state or a sector of the state. The amendments would require
units of state and local government, businesses, and individuals statewide
that own or operate model year 2004 and subsequent non-road LSI engines of
25 hp and larger, and all equipment and vehicles that use such engines to
use LSI engines certified under 13 CCR 9 as adopted by the CARB on October
19, 1999. The increased cost of $100 to $500 per engine would not cause material
impact given the high total cost of this type of equipment.
These rules do not exceed an express standard set by federal law, since
they implement requirements of the FCAA. Under 42 USC, §7410, states
are required to adopt a SIP which provides for "implementation, maintenance,
and enforcement" of the primary NAAQS in each air quality control region of
the state. These rules were specifically developed as part of an overall control
strategy to meet the ozone NAAQS set by the EPA under 42 USC, §7409.
While 42 USC, §7410 does not require specific programs, methods, or reductions
in order to meet the standard, state SIPs must include "enforceable emission
limitations and other control measures, means or techniques (including economic
incentives such as fees, marketable permits, and auctions of emissions rights),
as well as schedules and timetables for compliance as may be necessary or
appropriate to meet the applicable requirements of this chapter," (meaning
42 USC, Chapter 85, Air Pollution Prevention and Control). It is true that
42 USC does require some specific measures for SIP purposes, like the inspection
and maintenance program, but those programs are the exception, not the rule,
in the SIP structure of 42 USC. The provisions of 42 USC recognize that states
are in the best position to determine what programs and controls are necessary
or appropriate in order to meet the NAAQS. This flexibility allows states,
affected industry, and the public, to collaborate on the best methods for
attaining the NAAQS for the specific regions in the state. Even though 42
USC allows states to develop their own programs, this flexibility does not
relieve a state from developing a program that meets the requirements of §7410.
In order to avoid federal sanctions, states are not free to ignore the requirements
of §7410 and must develop programs to assure that the nonattainment areas
of the state will be brought into attainment on schedule. Thus, while specific
measures are not prescribed, both a plan and emission reductions are required
to assure that the nonattainment areas of the state will be able to meet the
attainment deadlines set by the FCAA. The EPA has provided the criteria for
both the submission and evaluation of attainment demonstrations developed
by states to comply with the FCAA. This criteria requires states to provide,
in addition to other information, photochemical modeling and an analysis of
specific emission reduction strategies necessary to attain the NAAQS. The
commission's photochemical modeling and other analysis indicate that substantial
emission reductions from both mobile and point source categories are necessary
in order to demonstrate attainment. In this case, this rulemaking is intended
to achieve emission reductions in the HGA nonattainment area. Specifically,
as noted elsewhere in this rule preamble, the emission reductions associated
with these rules are a necessary element of the attainment demonstration required
by the FCAA.
In addition, 42 USC, §7502(a)(2), requires attainment as expeditiously
as practicable, and 42 USC, §7511a(d), requires states to submit ozone
attainment demonstration SIPs for severe ozone nonattainment areas such as
HGA. By policy, the EPA requires photochemical grid modeling to demonstrate
whether the 42 USC, §7511a(f), NO
x
measures
would contribute to ozone attainment. The commission has performed photochemical
grid modeling which predicts that NO
x
emission
reductions, such as those required by these rules, will result in reductions
in ozone formation in the HGA ozone nonattainment area and help bring HGA
into compliance with the air quality standards established under federal law
as NAAQS for ozone. The 42 USC, §7511a(f), exemption from NO
x
measures for HGA expired on December 31, 1997. The expiration of
the exemption under 42 USC, §7511a(f), was based on the finding that
NO
x
reductions in HGA are necessary for attainment
of the ozone standard. Therefore, the adopted amendments are necessary components
of and consistent with the ozone attainment demonstration SIP for HGA, required
by 42 USC, §7410.
During the 75th Legislative Session, Senate Bill (SB) 633 amended the Texas
Government Code to require agencies to perform a regulatory impact analysis
(RIA) of certain rules. The intent of SB 633 was to require agencies to conduct
a RIA of extraordinary rules. With the understanding that this requirement
would seldom apply, the commission provided a cost estimate for SB 633 that
concluded "based on an assessment of rules adopted by the agency in the past,
it is not anticipated that the bill will have significant fiscal implications
for the agency due to its limited application." The commission also noted
that the number of rules that would require assessment under the provisions
of the bill was not large. This conclusion was based, in part, on the criteria
set forth in the bill that exempted proposed rules from the full analysis
unless the rule was a major environmental rule that exceeds a federal law.
As previously discussed, 42 USC does not require specific programs, methods,
or reductions in order to meet the NAAQS; thus, states must develop programs
for each nonattainment area to ensure that area will meet the attainment deadlines.
Because of the ongoing need to address nonattainment issues, the commission
routinely proposes and adopts SIP rules. The legislature is presumed to understand
this federal scheme. If each rule proposed for inclusion in the SIP was considered
to be a major environmental rule that exceeds federal law, then every SIP
rule would require the full RIA contemplated by SB 633. This conclusion is
inconsistent with the conclusions reached by the commission in its cost estimate
and by the Legislative Budget Board (LBB) in its fiscal notes. Because the
legislature is presumed to understand the fiscal impacts of the bills it passes,
and that presumption is based on information provided by state agencies and
the LBB, the commission believes that the intent of SB 633 was only to require
the full RIA for rules that are extraordinary in nature. While the SIP rules
will have a broad impact, that impact is no greater than is necessary or appropriate
to meet the requirements of 42 USC.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
It is presumed that "when an agency interpretation is in effect at the time
the legislature amends the laws without making substantial change in the statute,
the legislature is deemed to have accepted the agency's interpretation."
The commission's interpretation of the RIA requirements is also supported
by a change made to the Texas Administrative Procedure Act (APA) by the legislature
in 1999. In an attempt to limit the number of rule challenges based upon APA
requirements, the legislature clarified that state agencies are required to
meet these sections of the APA against the standard of "substantial compliance."
Texas Government Code, §2001.035. The legislature specifically identified
Texas Government Code, §2001.0225 as falling under this standard. The
commission has substantially complied with the requirements of §2001.0225.
Therefore, in addition to not exceeding an express standard set by federal
law, these rules do not exceed state requirements, and are not adopted solely
under the general powers of the agency because the provisions of the TCAA, §§382.011,
382.012, 382.017, 382.019, 382.039, and 382.051(d) authorize the commission
to implement a plan for the control of the states air quality, including measures
necessary to meet federal requirements. The remaining applicability criteria,
pertaining to exceeding a delegation agreement or contract between the state
and the federal government does not apply. Thus, the commission is not required
to conduct an RIA as provided in Texas Government Code, §2001.0225.
TAKINGS IMPACT ASSESSMENT
The commission evaluated this rulemaking action and performed an analysis
of whether the proposed rules are subject to Texas Government Code, Chapter
2007. The following is a summary of that analysis. The specific purposes of
these amendments are: to develop a new attainment demonstration SIP for the
ozone NAAQS for HGA; and to establish emission requirements on model year
2004 and subsequent non-road, LSI engines 25 hp and larger and all equipment
and vehicles that use such engines by requiring these engines to be certified
under 13 CCR 9 throughout the state.
This rulemaking action will act as an air pollution control strategy to
reduce NO
x
emissions in the ozone nonattainment
areas so that they may demonstrate attainment with the ozone NAAQS and maintain
air quality in near nonattainment areas across the state. Promulgation and
enforcement of these rules will not burden private, real property. Although
these rules do not directly prevent a nuisance or prevent an immediate threat
to life or property, they do prevent a real and substantial threat to public
health and safety, and partially fulfill a federal mandate under 42 USC, §7410.
Specifically, the emissions limitations and delays within these rules were
developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409.
States are primarily responsible for ensuring attainment and maintenance of
the NAAQS once the EPA has established them. Under 42 USC, §7410 and
related provisions, states must submit, for EPA approval, SIPs that provide
for the attainment and maintenance of NAAQS through control programs directed
to sources of the pollutants involved. Therefore, the purpose of these rules
is to implement a cleaner-burning, non-road, LSI engine program necessary
for the entire state to meet air quality standards established under federal
law as NAAQS. Consequently, the exemption which applies to these rules is
that of an action reasonably taken to fulfill an obligation mandated by federal
law. Therefore, this rulemaking action will not constitute a taking under
the Texas Government Code, Chapter 2007.
Also, Texas Government Code, §2007.003(b)(13), states that Chapter
2007 does not apply to an action that: 1) is taken in response to a real and
substantial threat to public health and safety; 2) is designed to significantly
advance the health and safety purpose; and 3) does not impose a greater burden
than is necessary to achieve the health and safety purpose. Although the rule
revisions do not directly prevent a nuisance or prevent an immediate threat
to life or property, they do prevent a real and substantial threat to public
health and safety and significantly advance the health and safety purpose.
In addition, §2007.003(b)(4) provides that Chapter 2007 does not apply
to these adopted rules since it is reasonably taken to fulfill an obligation
mandated by federal law. The amendments will implement requirements of 42
USC, §7410. This action is taken in response to the HGA area exceeding
the NAAQS for ground-level ozone, which adversely affects public health, primarily
through irritation of the lungs. The action significantly advances the health
and safety purpose by reducing ambient NO
x
and
ozone levels in HGA. Attainment of the ozone standard will eventually require
substantial NO
x
reductions. Any NO
x
reductions resulting from the current rulemaking are no greater than
what the best scientific research indicates is necessary to achieve the desired
ozone levels. However, this rulemaking action is only one step among many
necessary for attaining the ozone standard.
The commission has included elsewhere in this preamble its reasoned justification
for adopting this strategy and has explained why it is a necessary component
of the SIP, which is federally mandated. This discussion, as well as the HGA
SIP which is being adopted concurrently, explains in detail that every rule
in the HGA SIP package is necessary and that none of the reductions in those
packages represent more than is necessary to bring the area into attainment
with the NAAQS. For these reasons the rules do not constitute a takings under
Chapter 2007 and do not require additional analysis. Comments received during
the comment period regarding the takings impact assessment (TIA) are addressed
in the ANALYSIS OF TESTIMONY section of this preamble.
COASTAL MANAGEMENT PROGRAM CONSISTENCY REVIEW
The commission determined that this rulemaking action relates to an action
or actions subject to the Texas Coastal Management Program (CMP) in accordance
with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources
Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter
281, Subchapter B, Consistency with the Texas Coastal Management Program.
As required by 31 TAC §505.11(b)(2) and 30 TAC §281.45(a)(3), relating
to actions and rules subject to the CMP, commission rules governing air pollutant
emissions must be consistent with the applicable goals and policies of the
CMP. The commission reviewed this rulemaking action for consistency with the
CMP goals and policies in accordance with the rules of the Coastal Coordination
Council, and determined that this rulemaking action is consistent with the
applicable CMP goals and policies. The primary CMP policy applicable to this
rulemaking action is the policy that commission rules comply with regulations
at 40 Code of Federal Regulations (CFR) to protect and enhance air quality
in the coastal area. The rules, which require additional reductions of air
emissions in HGA, will result in reductions of ambient NO
x
and ozone concentrations. These rules are consistent with the applicable
CMP policy because they are consistent with 40 CFR. Title 40 CFR, Part 51,
sets out requirements for states to prepare, adopt, and submit implementation
plans for the attainment of the NAAQS. The adopted rules would be submitted
to the EPA under these requirements. No comments were received during the
comment period regarding the CMP.
HEARINGS AND COMMENTERS
The commission held public hearings on this proposal at the following times
and locations: September 18, 2000, in Conroe and Lake Jackson; September 19,
2000, in Houston (two hearings); September 20, 2000, in Katy and Pasadena;
September 21, 2000, in Beaumont, Amarillo, and Texas City; September 22, 2000,
in Dayton, El Paso, and Arlington; September 25, 2000, in Austin and Corpus
Christi. The comment period closed on September 25, 2000.
The following 46 commenters provided written or oral testimony on this
proposal: the City of Fort Worth (Fort Worth); the City of Lake Jackson (Lake
Jackson); the League of Women Voters of Texas (LWV-TX); Hispanic Community
for Texas Citizens for a Sound Economy (TCSE-HC); American Road and Transportation
Builders Association (ARTBA); Baker Botts; Business Coalition for Clean Air
(BCCA); Dow Chemical Company (Dow); Dynegy Inc. (Dynegy); the EPA; ExxonMobil
Corporation (ExxonMobil); Hanover Compressor Company (Hanover); Harris County
Judge Robert Eckels (Harris County); the City of Missouri City (Missouri City);
Phillips 66 Company (Phillips 66); Reliant Energy, Inc. (REI); RMT, Inc. on
behalf of Montgomery County (Montgomery Co.); Sierra Club Houston Regional
Group (Sierra-Houston), and 28 individuals.
Fort Worth, Lake Jackson, LWV-TX; and ten individuals supported the proposed
revisions, while the TCSE-HC; and four individuals opposed the proposed revisions.
The ARTBA, Baker Botts, BCCA, Dow, Dynegy, the EPA, ExxonMobil, Hanover, Harris
County, Missouri City, Phillips 66, REI, Montgomery Co., Sierra-Houston, and
five individuals supported the proposed revisions, but suggested changes or
clarifications as stated in the ANALYSIS OF TESTIMONY section of this preamble.
ExxonMobil adopted the BCAA comments by reference, and Dow and one individual
supported the BCCA comments.
ANALYSIS OF TESTIMONY
Sierra-Houston, LWV-TX, and one individual stated that all of these rules
should be applied statewide. Sierra-Houston commented that these rules should
be applied statewide so that maximum reductions in transboundary air pollution
can be made and so that county boundaries cannot be used to avoid adherence
to these rules. LWV-TX commented that SIP strategies that exceed those required
by the EPA should be adopted.
The commission appreciates the commenters' support for state-wide applicability
of these rules. The commission notes, however, that it is not obligated to
adopt all rules statewide in order to satisfy its commitments under the SIP,
nor is the commission required to do so under 42 USC. Three of the proposed
measures contain emission reduction strategies that have been proposed for
state-wide applicability: California LSI engines; emissions banking and trading
(that portion of the proposed rules which relates to the trading of emission
reduction credits and discrete emission reduction credits); and low emission
diesel fuel (that portion of the proposed rules which relates to on-road fuel).
In evaluating whether to implement all of the rules statewide, the commission
took into account many concerns, including but not limited to, the need for
the marketplace to be able to respond to regulation, the possible impacts
on transport and distribution systems, the possibility of increased costs
and financial burdens on regulated entities, and regional needs and issues
associated with state-wide mandates. The commission also analyzed where emission
reduction measures are most needed and where emission reduction measures will
be most effective in order to demonstrate attainment.
Sierra-Houston resubmitted comment letters dated August 2, 1999, January
31, 2000, and February 24, 2000 concerning already-completed rulemakings and
SIP revisions which Sierra-Houston had initially submitted during the comment
period for these previous rulemakings and SIP revisions.
These comments were addressed in the ANALYSIS OF TESTIMONY section of the
preambles to the earlier rulemakings and SIP revisions which were published
in previous issues of the
Texas Register.
One individual commented that the proposed rules are designed to embarrass
the governor, and that the Texas Legislature and Congress should analyze these
plans.
The commission's intent is not to embarrass Texas and the governor, but
instead to comply with the timelines provided in the 1990 FCAA amendments
and subsequent EPA guidance for submitting rules to demonstrate ozone attainment
in HGA. Accordingly, Texas has committed to adopting the majority of the necessary
rules for the HGA attainment demonstration by December 31, 2000.
One individual stated opposition to tractor restrictions being applied
to rural counties like Chambers and Liberty, because those counties add nothing
to the pollution problem.
These rules apply to all counties throughout the state including Chambers
and Liberty County. However, engines less than 175 hp used in agriculture
and construction are exempt from these rules, so those living in rural counties
who operate tractors with engines rated at less than 175 hp will not be affected
by these rules.
One individual commented that recreational equipment should not be exempt
from these rules, and another individual commented that no equipment should
be exempted from these rules.
The commission appreciates the commenter interest in protecting air quality
by suggesting inclusion of all equipment, including recreational equipment,
in the scope of these rules. However, the commission disagrees with the suggestion
that no equipment should be exempt from these rules, including recreational
vehicles. The amendments to these rules incorporate by reference the California
non-road, LSI engine rule because 42 USC requires that the Texas program be
identical to the California non-road LSI program. Although emissions from
non-road, LSI engines have not yet been regulated by the EPA, the CARB has
adopted exhaust emission standards for these engines. These rules and amendments
will apply throughout the State of Texas.
One individual commented that the phasing out of equipment should be a
longer period so that small farmers or small business owners are not adversely
affected.
These rules do not require an immediate phase-out of equipment. Rather,
these rules require that any equipment which is replaced beginning in model
year 2004 must be CARB-certified. Small farmers and small business owners
should not experience financial harm from these rules because the CARB-certified
engines are estimated to cost an additional $100 - $500 per piece of equipment.
No significant fiscal implications are anticipated to individuals, state and
local government agencies, and businesses statewide that own or operate affected
equipment powered by LSI engines as a result of implementing these rules,
unless a business or individual replaces between 200 and 1,000 of these engines
annually.
One individual commented that fleet vehicles should not be required to
meet the California emission standards.
These rules cover non-road LSI engines rated 25 hp or over, or equipment
that uses engines of that size, whether or not the engines or equipment are
to be used in a fleet. Non-road LSI engines over 25 hp are primarily used
to power industrial equipment such as forklifts, generators, pumps, compressors,
aerial lifts, sweepers, and large lawn tractors. Texas has chosen to adopt
the California standards because they are more stringent than the current
engine standards in place in Texas, and because implementation of the California
standards is estimated to provide at least 2.8 tpd of NO
x
-equivalent reductions which are needed in order for the HGA nonattainment
area to achieve the ozone NAAQS by 2007. The extension of these rules to all
counties in the state should also contribute to maintenance of the one-hour
ozone standard in the rest of the state.
One individual commented that all equipment manufactured by Briggs and
Stratton will meet the CARB emission standards. The individual stated that
the engines already have a spark-advanced system, and that Briggs and Stratton
will continue to follow California emission standards.
The commission is pleased to hear that companies such as Briggs and Stratton
are complying with the California standards at this time and encourages Briggs
and Stratton to continue to do so.
One individual commented that the registration of and pollution tax on
engines over 24 hp is long overdue, and is necessary to determine the contribution
of their emissions to the HGA ozone precursor problem.
The commission agrees with the commenter that these rules are necessary.
However, these rules do not require the registration of, nor levy a tax on
all engines 25 hp and greater. Rather, the rules require that non-road, LSI
engines 25 hp or greater produced in model year 2004 and subsequent, be CARB-certified.
One individual commented that "these rules go far beyond anything necessary
to protect the environment." The individual also commented that the basis
and analysis for these rules is flawed. One individual added that the "guess"
models are an insufficient basis upon which to base policy decisions and regulations,
and that emission curtailment is necessary due to the long operational life
of these engines.
The commission disagrees with the first three comments. The HGA is classified
as a "severe" nonattainment area under 42 USC. If the commission were to propose
a SIP with less stringent emission reductions, the HGA could face penalties
from the federal government, including the loss of federal highway funds.
In order to avoid such penalties, the commission has worked with all stakeholders
to attempt to formulate strategies that can reduce emissions to levels that
will satisfy the requirements of 42 USC. The current SIP revision contains
photochemical modeling analysis in support of the HGA ozone attainment demonstration
that meets all EPA criteria. Modeling staff used the latest technology to
estimate emission levels across the state and has worked with EPA to study
the air pollution dilemma in the HGA area. The commission estimates that this
control measure will achieve a minimum of 2.8 tpd of NO
x
-equivalent reductions and is therefore a necessary measure to successfully
demonstrate attainment. The commission agrees that emission curtailment is
necessary to help reduce NO
x
.
One individual applauded the commission for passing rules related to more
efficient engines, but asked that the commission not force people to do things
they can't afford.
The commission appreciates the commenter's support for these rules related
to engine efficiency. The commission is uncertain whether the commenter's
monetary concern is for private individuals or businesses. These rules will
not affect the average citizen, unless he or she uses LSI engines rated at
or above 25 hp and the engines are not exempted under these rules. These engines
are mainly used for industrial operations. There are no significant fiscal
implications anticipated to individuals, state and local government agencies,
and businesses statewide that own or operate affected equipment powered by
LSI engines as a result of implementing these amendments unless a business
or individual replaces between 200 and 1,000 of these engines annually. It
is unlikely that the average citizen will replace a large quantity of these
types of engines annually.
Fort Worth commented that it appreciates the efforts of the City of Houston
and its regional partners in submitting a proposed SIP that is compliant with
the 42 USC mandates because the DFW region is affected by the pollution generated
in the HGA. Fort Worth also commented that it appreciates the commission efforts
to enlarge the markets for affected LSI engines by applying these rules statewide.
The commission appreciates the commenter's support. The entire state will
benefit from reduction of NO
x
emissions and from
the greater economy of scale. State-wide emission reductions help attainment
areas maintain attainment status while assisting nonattainment areas in controlling
and reducing NO
x
emissions.
One individual commented that the California LSI engine rules should apply
to all internal combustion engines in the HGA and the state. Dow commented
that these rules do not make clear which equipment is included and asked the
commission to clarify whether a diesel engine is of the LSI category.
Diesel engines are not affected by these rules. Diesel engines are classified
as compression-ignition engines, not spark-ignition engines. Spark-ignition
engines run on gasoline, not diesel fuel, therefore these rules do not apply
to all internal combustion engines. The amendments to these rules incorporate
by reference the California non-road, LSI engine rule, which does not apply
to all internal combustion engines. These rules are identical to the rules
effective in California because 42 USC requires that the Texas program be
identical to the California non-road LSI program. Although emissions from
non-road, LSI engines have not yet been regulated by the EPA, the CARB has
adopted exhaust emission standards for these engines. These rules will apply
throughout the State of Texas.
EPA commented that the statement relating to the incorporation by reference
into the HGA SIP of future revisions to the California regulations should
be removed as was done in the DFW SIP. Hanover commented that it understood
these rules to state that all future amendments that may be passed in California
will be adopted and incorporated into the Texas rules.
The EPA is correct. The preamble of these rules as published for proposal
in the
Texas Register
contained two statements
relating to the incorporation by reference into the Texas rules of all future
revisions to the California regulations. Although the commission believes
it has authority to adopt all future revisions by reference, the two statements
relating to incorporation by reference of all future revisions have been removed
from the preamble. The commission has deleted the statements relating to incorporation
by reference to allow greater consideration of each change made by California
prior to adoption of a change in Texas.
Lake Jackson commented that it can replace by 2007 its two pieces of equipment
covered under these rules. Missouri City commented that it would experience
increased costs associated with the purchase of new vehicles for the city
fleet and the modification of existing equipment.
Lake Jackson may use the equipment it has on hand until the year 2007 and
still remain in compliance with these rules. In fact, Lake Jackson and Missouri
City can continue to use the equipment already on hand until that equipment
fails and must be replaced whether that is in 2004, 2007, or beyond. If the
equipment is replaced beginning in model year 2004 any new equipment using
a non-road LSI engine must be CARB-certified. As noted elsewhere in this ANALYSIS
OF TESTIMONY, these rules require model year 2004 and subsequent non-road,
LSI engines 25 hp and larger to be certified under 13 CCR 9. Therefore, Missouri
City will not be required to modify existing equipment. Furthermore, Missouri
City should not experience significant increased costs associated with the
purchase of new vehicles unless it replaces between 200 and 1,000 vehicles
per year, because the estimated additional cost of the CARB-certified LSI
engine is approximately $100 - $500 per vehicle. Finally, these rules do not
apply to on-road vehicles.
One individual supported stricter automobile emission standards and would
approve of a proposal making trucks and sport utility vehicles (SUV) meet
California LSI standards.
The commission appreciates the commenter's enthusiasm for stricter emission
standards. The commission notes, however, that these rules apply only to non-road
engines. The commenter seems to be registering support for stricter standards
for on-road trucks and SUVs. The EPA has adopted the Tier II standards which
require most trucks and SUVs to meet emission standards similar to light-duty
gasoline automobiles.
One individual commented that "non-road engine strategies" would bankrupt
businesses and undermine family lives.
The commission does not believe that these rules will have the negative
financial impact predicted by the commenter. No significant fiscal implications
are anticipated to individuals, state and local government agencies, and businesses
statewide, unless an entity replaces between 200 and 1,000 of these engines
annually. The CARB has determined the exhaust emission standards for non-road,
LSI engines to be technologically feasible and a cost-effective strategy at
$.25 per pound ($500 per ton) of NO
x
and HC reduced,
that will move the state toward reducing NO
x
and HC from non-road, LSI engines.
ARTBA commented on six proposed rules collectively calling them the "proposed
construction rules." ARTBA included California LSI engine standards in this
group. ARTBA stated that these rules will threaten public and occupational
safety, and that these rules will create negative social and economic effects
which the commission has not studied.
The commission first notes that although ARTBA included the California
LSI engine rules in its general category of proposed construction rules, ARTBA
acknowledged that the FCAA expressly preempts all of the proposed construction
rules except the California LSI standards. This statement implies that ARTBA's
comments are focused on the remaining five proposed rules it includes in the
proposed construction rules, not on the California LSI engine proposed rule.
ARTBA stated elsewhere in its comments that only California may adopt standards
or requirements relating to non-road vehicles, and ARTBA observes that only
the commission's LSI standards follow the prescribed FCAA §209(e) procedures
for adopting nonroad emissions regulations. ARTBA noted that "if and only
if California does so, other states may then mirror California's actions,
but may not deviate from them." The LSI engine rules mirror California's rules,
as explained elsewhere in this ANALYSIS OF TESTIMONY.
Assuming that ARTBA's comments were intended to express ARTBA's belief
that the California LSI engine rules will "threaten public and occupational
safety, and create negative social and economic effects which the commission
has not studied, the commission does not agree that these rules will have
the negative impacts predicted by ARTBA. These rules will, to the contrary,
prevent a real and substantial threat to public health and safety via the
reduction of air pollution, and partially fulfill a federal mandate under
42 USC, §7410. Specifically, the emissions limitations and delays within
these rules were developed in order to meet the ozone NAAQS set by the EPA
under 42 USC, §7409.
The commission disagrees that possible negative social and economic effects
of these rules have not been studied. There are no significant fiscal implications
anticipated to individuals, state and local government agencies, and businesses
statewide that own or operate affected equipment powered by LSI engines as
a result of implementing these rules and amendments unless an entity replaces
between 200 and 1,000 of these engines annually. The CARB has determined the
exhaust emission standards for non-road, LSI engines to be technologically
feasible and a cost-effective strategy at $.25 per pound ($500 per ton) of
NO
x
and HC reduced, that will move the state
toward reducing NO
x
and HC from non-road, LSI
engines.
ARTBA encouraged the commission to consider adopting incentive programs
to reduce mobile source emissions from both on-road motor vehicles and non-road
vehicles, and to adopt both incentive programs and command and control regulations
on stationary sources.
The commission agrees that economic incentive programs can potentially
be an effective tool for achieving air quality. One such program is the Carl
Moyer program in California. That program appears to be successful in providing
flexibility to the regulated industry while still achieving reductions in
air emissions. The California program is authorized by and funded through
the state legislative process and such legislative approval does not currently
exist for a similar Texas program. The commission will continue to try to
identify economic incentives which it has authority to implement. Because
the commission agrees that market-based incentive programs can be an important
component in encouraging development of new technologies and/or greater or
more cost effective emission reduction strategies, the commission has provided
for the inclusion of economic incentive programs as a component of the HGA
SIP in the future.
Hanover requested clarification as to whether the type of engine it uses
(minor source semi-portable compressor engines) is exempted from these rules,
and whether an exemption can be added to these rules for clarity. Hanover
believed that minor source semi-portable compressor engines should be exempted
due to their short projected useful life. Hanover also noted that the control
systems required by these rules would involve costs of development, implementation,
and maintenance far beyond the estimates contained in the proposal.
The type of engine to which Hanover refers is the type of engine intended
to be regulated by this proposed rule, therefore no exemption will be added
to the rules. The commission disagrees that semi-portable compressor engines
should be excluded from these rules based upon the length of their projected
useful life because these are precisely the types of engines that the commission
is seeking to include in these rules. The commission cannot exempt these engines
because these rules must remain identical to the California rule. The following
is quoted from an EPA Engine Programs and Compliance Division Memorandum dated
January 29, 1999, titled
California Requirements
for Large SI Engines and Possible EPA Approaches:
"Upgrading to modern
engine technologies greatly improves the capability of these engines to control
emissions and will generally improve engine performance. Electronically-controlled
closed-loop operation also provides the potential for great improvement in
engine operation. For example, improving control of combustion may allow a
fuel economy improvement of 15% to 20%. Also, feedback control of air-fuel
ratios eliminates much of the need to maintain and adjust a large number of
fuel system calibrations, resulting in reduced product inventories and, more
importantly, less downtime and maintenance for equipment in the field. Finally,
improved control of the upgraded engines should lead to significantly longer
engine lifetimes. The net present value of these benefits would likely be
considerably greater than the incremental cost of improving the engines."
No significant fiscal implications are anticipated to negatively impact
individuals, state and local government agencies, and businesses statewide
that own or operate affected equipment powered by LSI engines as a result
of implementing the proposed amendments unless an entity replaces between
200 and 1,000 of these engines annually.
Montgomery Co. commented that it should be excluded from these rules based
on its assumption that exclusion of this area would result in a difference
of less than 1/1000th (0.001) of a part per billion of ozone. One individual
stated opposition to these rules being applied to counties like Chambers and
Liberty, because those counties add "nothing" to the pollution problem.
The FCAA Amendments of 1990 provided new requirements for areas that had
not attained the NAAQS for ozone, carbon monoxide, particulate matter, sulfur
dioxide, nitrogen dioxide, and lead, and new requirements for SIPs in general.
The EPA was authorized to designate areas failing to meet the NAAQS for ozone
as nonattainment and to classify them according to severity. The FCAA, §107(d)(4)(A)(iv)
mandated that areas designated as serious, severe, or extreme for ozone that
were within a metropolitan statistical area (MSA) or CMSA must have boundaries
that include the entire MSA or CMSA. This requirement is supported by the
legislative history for the 1990 FCAA Amendments in Senate Report No. 101-228,
page 3399, "because ozone is not a local phenomenon but is formed and transported
over hundreds of miles and several days, localized control strategies will
not be effective in reducing ozone levels. The bill, thus, expands the size
of areas that are defined as ozone nonattainment areas to assure that controls
are implemented in an area wide enough to address the problem." The 1990 FCAA
Amendments did provide the ability to exclude portions of the entire MSA or
CMSA prior to designation, if the state conducted a study, to which the EPA
agreed, that proved the geographic portion did not contribute significantly
to violation of the NAAQS.
Redesignation has not occurred for any portion of the HGA nonattainment
area, and is not currently being considered. For existing areas currently
included within a nonattainment area, the specific area must be redesignated
as attainment in order to be removed from a nonattainment area. The FCAA, §107(d)(3)
provides that the EPA may not redesignate a nonattainment area, or a portion
of a nonattainment area, to attainment unless several criteria are met. These
criteria include: a determination that the area has attained the NAAQS; there
is a fully approved SIP for the area; there is a determination that the improvement
in air quality is due to permanent and enforceable emissions reductions; there
is an approved maintenance plan for the area; and the state has met all requirements
for the area under FCAA, §110 and Part D.
However, even if a specific area within the HGA nonattainment area was
redesignated by the EPA as attainment for ozone, reductions associated from
all adopted ozone control strategies would still be necessary, because of
the requirements of FCAA, §107(d)(3) and §175A which require maintenance
plans for all redesignated areas. The maintenance plan must include the measures
specified in §107(d)(3) and any additional measures that are necessary
to ensure that the area continues to be in attainment with the NAAQS for ten
years after the redesignation. Eight years after the redesignation, the state
is required to submit an additional SIP revision to maintain the NAAQS for
another ten years after the end of the first ten-year period.
Additionally, reductions associated from the ozone control strategies that
will be implemented outside the HGA nonattainment area will benefit the HGA
nonattainment area. This is due to the regional nature of air pollution, the
contribution from mobile sources, and the economies of scale and associated
market advantages related to distribution networks for some strategies.
At the time the 1990 FCAA Amendments were enacted, the focus on controlling
ozone pollution was centered on localized controls. However, for many years
an ever increasing number of air quality professionals have concluded that
ozone is a regional problem requiring regional strategies in addition to local
control programs. As nonattainment areas across the United States prepared
attainment demonstration SIPs in response to the 1990 FCAA Amendments, several
areas found that modeling attainment was made much more difficult, if not
impossible, due to high levels of ozone and ozone precursor entering from
the boundaries of their respective modeling domains, commonly called transport.
Recent science indicates that regional approaches may provide improved control
of ozone air pollution.
The commission has conducted air quality modeling and upper air monitoring
that found regional air pollution should be considered when studying air quality
in the Texas ozone nonattainment areas. This work is supported by research
conducted by the OTAG, the most comprehensive attempt ever undertaken to understand
and quantify the transport of ozone. Both the commission and the OTAG study
point to the need to take a regional approach to controlling air pollutants.
REI commented that the emission limitations have been developed with a
less than complete analysis of the technical or economic feasibility, inaccurate
cost estimates, and a less than complete analysis of the possible environmental
or economic disbenefit of the controls. One individual commented that the
rules may harm economic growth.
The commission disagrees with the comments and made no change in response
to these comments. The proposed rules contained an analysis of information
available to the commission regarding the costs and benefits of the proposed
rules. This information met the statutory requirements of the TCAA and the
Texas Administrative Procedure Act (APA) because the information provided
in the proposed rules was sufficient for commenters to submit alternative
assessments of the costs and benefits.
Adequate notice is essential for fairness as well as a meaningful opportunity
to comment on proposed rules.
United Loans, Inc.
v. Pettijohn,
955 S.W.2d 649, 651 (Tex. App.-Austin 1997). To achieve
the goal of encouraging meaningful public participation in the formulation
and adoption of rules by state agencies, the notice must have sufficient information
so that interested persons can determine whether it is necessary for them
to participate in order to protect their legal rights and privileges. The
commission received intelligent comments which were substantial in both number
and in scope, regarding the costs of the proposed rules and the technical
practicability of compliance. Therefore, the commission believes this goal
has been achieved and that the notice includes sufficient information to constitute
adequate notice.
The purpose of the comment period is for the public to provide the commission
with information to say why they agree or disagree. To simply state that the
proposal did not meet the statute or that compliance with the proposed rules
is not technically or economically feasible does not provide the commission
with sufficient information to propose changes or alternative strategies.
There is no requirement that the commission determine the probable economic
cost of the unique aspects of every facility or source that must comply, nor
give the probable economic cost of every possible method of control. Rather,
the notice must include the cost of a reasonable method of compliance. Mere
disagreement with cost or technical feasibility estimates does not render
notice inadequate.
The rule proposal met the requirement to include sufficient information,
because it provided an explanation of the costs associated with implementation
of the rule requirements, as well as the date upon which CARB-certified engines
must be made available for purchase. To simply state that the proposal failed
to provide sufficient information does not provide the commission with sufficient
information to propose changes or alternative strategies. The commenters did
not say how the notice is insufficient, merely that it is insufficient. Nevertheless,
the commission reviewed the notice and determined it to have been adequate.
The commission responses to comments regarding costs of compliance with these
rules are discussed in the FINAL REGULATORY IMPACT ANALYSIS DETERMINATION
section of this preamble and throughout this ANALYSIS OF TESTIMONY. The commission
response to technical feasability of these rules is also discussed in the
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE ADOPTED RULE section of
this preamble and throughout this ANALYSIS OF TESTIMONY.
One individual commented that the rule package does not contain any information
concerning the effectiveness of this equipment, therefore the individual would
like to see a pilot program initiated before these rules are adopted.
The commission will not be performing a pilot program due to the success
of these rules in California. The commission is relying on data obtained by
the CARB to justify the effectiveness of these rules, which the commission
is entitled to do because of the need for the Texas program to remain identical
to the California program. With respect to effectiveness of equipment, the
following is quoted from an EPA Engine Programs and Compliance Division Memorandum
dated January 29, 1999, titled
California Requirements
for Large SI Engines and Possible EPA Approaches:
"Upgrading to modern
engine technologies greatly improves the capability of these engines to control
emissions and will generally improve engine performance. Electronically-controlled
closed-loop operation also provides the potential for great improvement in
engine operation. For example, improving control of combustion may allow a
fuel economy improvement of 15% to 20%. Also, feedback control of air-fuel
ratios eliminates much of the need to maintain and adjust a large number of
fuel system calibrations, resulting in reduced product inventories and, more
importantly, less downtime and maintenance for equipment in the field. Finally,
improved control of the upgraded engines should lead to significantly longer
engine lifetimes. The net present value of these benefits would likely be
considerably greater than the incremental cost of improving the engines."
There are no significant fiscal implications anticipated to individuals, state
and local government agencies, and businesses statewide that own or operate
affected equipment powered by LSI engines as a result of implementing these
rules unless an entity replaces between 200 and 1,000 of these engines annually.
The commission estimates that this measure will achieve a minimum of 2.8 tpd
of NO
x
equivalent reductions and is therefore
a necessary measure for successfully demonstrating attainment.
These rules will go into effect without a pilot program due to the fact
that these rules and the others contained in the SIP package that pertain
to the HGA and the state are necessary for the HGA to meet attainment by 2007.
Furthermore, the commission has studied the results that California has experienced
with this program and is convinced of its effectiveness in reducing emissions
in a cost-effective manner.
Several individuals inquired about who would enforce these rules, and commented
that enforcement of the proposed rules will be difficult, impossible, and
expensive. One individual asked how the commission will ensure that the engines
affected by these rules will be inspected for compliance, because they do
not have to be inspected like those engines that are licensed for highway
use.
As with all of its rules, the commission will enforce the requirements
after the rule compliance date and take appropriate action for noncompliance
situations. The rules are enforced by staff in the commission's regional offices,
as well as local air pollution control programs. Local governments have the
same power and are subject to the same restrictions as the commission under
TCAA, §382.015, Power to Enter Property, to inspect the air and to enter
public or private property in its territorial jurisdiction to determine if
the levels of air contaminants meet levels set by the commission. Local governments
are not required to enforce commission rules, but may sign cooperative agreements
with the commission to enforce the rules under TCAA, §382.115, Cooperative
Agreements. Local programs can also enforce commission rules without signing
a cooperative agreement. The authority of local governments to enforce air
pollution requirements is specified in detail in TCAA, §§382.111
- 382.115, and local governments can institute civil actions in the same manner
as the commission under Texas Water Code (TWC), §7.351.
The commission will work with local officials to ensure enforcement of
the SIP and SIP rules. The commission has existing relationships with pollution
control authorities in the City of Houston, Harris County, and Galveston County
for enforcement of other commission rules. The commission will continue enforcement
relationships with these entities and develop relationships with other local
officials as needed to create effective enforcement mechanisms for the SIP
and SIP rules.
BCCA, Dynegy, ExxonMobil, Phillips 66, and REI stated that the proposed
rules did not include an adequate small business and micro-business assessment
as required under Texas Government Code, §2006.002. The commenters stated
that an analysis of the costs of compliance for small and micro-businesses
must also compare the costs of compliance for these businesses with the costs
for the largest businesses affected by these rules. The commenters stated
that the comparison must use at least one of the following standards: cost
for each employee, cost for each hour of labor, or cost for each $100 of sales.
The commenters asserted that the rule proposal failed to include the mandated
cost comparison standards. The commenters stated that this is the case even
in those instances where the commission acknowledged a significant impact.
The commenters stated that the commission either restated the costs of compliance
it identified in the analysis of public benefits and costs, or concluded that
it cannot determine the cost to small businesses. The commenters stated that
the rule proposal preamble stated that "the estimated capital and annualized
cost of installing and operating control technology used for the various types
of equipment in the fiscal note would appear to be a reasonable cost estimate
for small and micro-businesses." (25 TexReg 8293).
The commenters asserted that the rule proposal assessments fall short of
what Texas law requires and that it is not sufficient for the commission merely
to state that the costs for small and large businesses will be the same. The
commenters stated that the rationale behind requiring a comparison using an
established standard, e.g., cost for each employee, cost for each hour of
labor, or cost for each $100 of sales, is to determine whether there is a
disparate impact on small businesses. The commenters stated that according
to
Unified Loans v. Pettijohn,
955 S.W.2d
at 652 (Court of Appeals -- Austin, 1997), the statute's purpose is to obtain
"an objective assessment of the agency's proposed action by forcing it to
consider seriously. . . the effect of these rules on small businesses, including
an analysis of their costs of compliance and a comparison of their costs with
the cost of compliance for the largest businesses affected . . . ." The commenters
stated further that the commission cannot merely conclude that the costs to
small businesses "cannot be determined," and is obliged to include in the
notice "some basis" for its conclusion so that interested parties can "confront
that basis in a meaningful way in their comments." (
Unified Loans v. Pettijohn,
955 S.W.2d at 653.)
The commenters stated that in the rule proposal preamble, the commission
did not publish the information mandated by Texas law and that as a result,
it is impossible for the public to comment on whether the agency adequately
considered the effect of these rules on small businesses, thus rendering the
notice of the plan inadequate. The commenters stated that Texas Government
Code, §2006.002, requires the commission to provide a comparison of the
proposed rule impact on small and large businesses, using the specified standards,
for public review and comment before adoption.
The commission estimated, to the extent possible, the costs to small businesses
and determined that the cost depends more upon the number of non-road engines
operated by the business, and that it is not dependent upon the number of
employees, hours of labor, or amount of sales income. Some small businesses
have only one piece of non-road equipment while others have large fleets.
Large businesses vary in the same way. The size of the fleet is not dependent
upon the size of the business. The commission provided the estimated cost
per piece of equipment and argues that this is the only meaningful way to
provide sufficient notice of the cost to small business and therefore that
it meets the objective of Texas Government Code, Chapter 2006. This assertion
is supported by the fact that no small businesses provided comments which
include cost of compliance in terms of the number of employees, hours of labor,
or amount of sales income.
ARTBA, BCCA, Dynegy, ExxonMobil, Phillips 66, and REI commented on the
draft RIA and stated that the proposed rules were not evaluated in accordance
with the analysis requirements for a major environmental rule. The commenters
stated that Texas Government Code, §2001.0225, requires an RIA for certain
major environmental rules. The commenters stated that the commission must
consider the benefits and costs of the proposed rules in relationship to state
agencies, local governments, the public, the regulated community, and the
environment. The commenters stated further that the commission must also incorporate
aspects of this analysis into the fiscal note in the proposed rules, e.g.,
identify the costs and the benefits; describe reasonable alternative methods
for achieving the purpose of these rules considered by the agency; provide
the reasons for rejecting those alternatives; and identify the data and methodology
used in performing the analysis. The commenters stated that under §2001.0225(d)
the commission must also find that "compared to the alternative proposals
considered and rejected, these rules will result in the best combination of
effectiveness in obtaining the desired results and of economic costs not materially
greater than the costs of any alternative regulatory method considered."
The commenters stated that the rule proposal preamble statement, that the
rules are exempt from the RIA requirement because federal law mandates the
rules, is a legally flawed effort to avoid an RIA and may render these rules
invalid. The commenters stated that federal law does not mandate the control
requirements, emission rates, and use restrictions contained in the proposal
and asserted that many of the proposed rules exceed specific federal rules
and standards applicable to the same sources. The commenters stated that examples
of departures from the federal framework include the following: boiler, turbine,
and other fired-equipment emission limits set well below federal new source
performance standards, reasonably available control technology, best available
control technology, or lowest achievable emission rate limits for the same
sources; and compressor engine emission limits set at unprecedented low levels
specifically designed to be unachievable and prevent the further use of the
affected engines.
The commenters stated that the rule proposal preamble acknowledges that
the rules are "major environmental rules," but that the commission asserted
that an RIA is "seldom" required and is only required for "extraordinary"
rules. The commenters stated that these criteria appear nowhere in the RIA
requirements. The commenters stated that the rule proposal preamble states
that "while the SIP rules will have a broad impact, that impact is no greater
than is necessary or appropriate to meet the requirements of the FCAA." The
commenters stated that this "no greater than is necessary or appropriate"
determination is the conclusion that an RIA is designed to evaluate and to
offer for public review and comment. The commenters stated that the rule proposal
is well beyond any federal mandates for the covered sources and are "extraordinary."
The commenters stated that under Texas Government Code, §2001.0225, an
RIA must be performed and offered for public comment before the proposal can
be adopted.
The commission disagrees with ARTBA, BCCA, Dynegy, ExxonMobil, Phillips
66, and REI that the rules are legally flawed. While the rules may require
those entities purchasing new CARB-certified LSI engines upon replacement
of worn out engines, that alone is not enough to trigger the RIA requirements.
The Texas Government Code, §2001.0225 only applies to a major environmental
rule adopted by a state agency, the result of which is to: 1) exceed a standard
set by federal law, unless the rule is specifically required by state law;
2) exceed an express requirement of state law, unless the rule is specifically
required by federal law; 3) exceed a requirement of a delegation agreement
or contract between the state and an agency or representative of the federal
government to implement a state and federal program; or 4) adopt a rule solely
under the general powers of the agency instead of under a specific state law.
This rulemaking action does not meet any of these four applicability requirements,
and is adopted in substantial compliance with the RIA requirements of Texas
Government Code, §2001.035. These rules do not exceed an express standard
set by federal law because the LSI non-road engine requirements are specifically
developed to meet the ozone NAAQS set by the EPA under 42 USC, §7409.
Title 42 USC, §7410 requires states to adopt a SIP which provides for
"implementation, maintenance, and enforcement" of the primary NAAQS in each
air quality control region of the state. While 42 USC, §7410 does not
specifically prescribe programs, methods, or reductions to meet the federal
standard, state SIPs must include "enforceable emission limitations and other
control measures, means or techniques (including economic incentives such
as fees, marketable permits, and auctions of emissions rights), as well as
schedules and timetables for compliance as may be necessary or appropriate
to meet the applicable requirements of this chapter" (meaning 42 USC, Chapter
85, Air Pollution Prevention and Control). The FCAA does require some specific
measures for SIP purposes, such as an inspection and maintenance program,
but those programs are the exception, not the rule, in the federal SIP structure.
The provisions of 42 USC recognize that states are in the best position to
determine what programs and controls are necessary or appropriate in order
to meet the NAAQS. This flexibility allows states, affected industry, and
the public to collaborate on the best methods for attaining the NAAQS for
the specific regions in the state. In order to avoid federal sanctions, states
are not free to ignore the requirements of 42 USC, §7410, and must develop
programs to assure that the nonattainment areas of the state will be brought
into attainment on schedule. Failure to develop control strategies to demonstrate
attainment can result in federal sanctions. Thus, while specific measures
are not prescribed, both a plan and emission reductions are required to assure
that the nonattainment areas of the state will be able to meet the attainment
deadlines set by 42 USC. The EPA has provided the criteria for both the submission
and evaluation of attainment demonstrations developed by states to comply
with 42 USC. This criteria requires states to provide, in addition to other
information, photochemical modeling and an analysis of specific emission reduction
strategies necessary to attain the NAAQS. The commission's photochemical modeling
and other analyses indicate that substantial emission reductions from both
mobile and point source categories are necessary in order to demonstrate attainment.
In this case, this rulemaking action is intended to achieve reductions in
ozone precursor emissions in the HGA nonattainment area. Specifically, as
noted elsewhere in this rule preamble, the emission reductions associated
with these rules are a necessary element of the attainment demonstration required
by 42 USC.
This conclusion is supported by the legislative history for Texas Government
Code, §2001.0225. During the 75th Legislative Session, SB 633 amended
the Texas Government Code to require agencies to perform an RIA of certain
rules. The intent of SB 633 was to require agencies to conduct a RIA of major
environmental rules that will have a material adverse impact, and will exceed
a requirement of state law, federal law, or a delegated federal program, or
are adopted solely under the general powers of the agency. The commission
provided a cost estimate for SB 633 that concluded "based on an assessment
of rules adopted by the agency in the past, it is not anticipated that the
bill will have significant fiscal implications for the agency due to its limited
application." The commission also noted that the number of rules that would
require assessment under the provisions of the bill was not large. Because
of the ongoing need to address nonattainment demonstrations required by federal
law, the commission routinely proposes and adopts SIP rules. If each rule
proposed for inclusion in the SIP was incorrectly considered as exceeding
federal law, every SIP rule would require the full RIA contemplated by SB
633. This result would be inconsistent with the cost estimates and fiscal
notes prepared by the commission and by the LLB. Since the legislature is
presumed to understand the fiscal impacts of the bills it passes, and that
presumption is based on information provided by state agencies and the LBB,
the commission believes that the intent of SB 633 was only to require the
full RIA for rules that meet the requirements under §2001.0225(a). While
the SIP rules will have a broad impact, that impact is no greater than is
necessary or appropriate to meet the requirements of 42 USC. In other words,
the rules are intended to meet federal and state law, and does not go above
and beyond what is required to meet federal or state statutes.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
It is presumed that "when an agency interpretation is in effect at the time
the legislature amends the laws without making substantial change in the statute,
the legislature is deemed to have accepted the agency's interpretation."
The commission's interpretation of the RIA requirements is also supported
by a change made to the APA by the legislature in 1999. In an attempt to limit
the number of rule challenges based upon APA requirements, the legislature
clarified that state agencies are required to meet these sections of the APA
against the standard of "substantial compliance." Texas Government Code, §2001.035.
The legislature specifically identified §2001.0225 as falling under this
standard. The commission has substantially complied with the requirements
of §2001.0225.
Therefore, in addition to not exceeding an express standard set by federal
law, these rules do not exceed state requirements, and are not adopted solely
under the general powers of the agency because the provisions of the TCAA, §§382.011,
382.012, 382.017, 382.019, and 382.039; authorize the commission to implement
a plan for the control of the states air quality, including measures necessary
to meet federal requirements. The remaining applicability criteria, pertaining
to exceeding a delegation agreement or contract between the state and the
federal government does not apply. Thus, the commission is not required to
conduct a regulatory analysis as provided in Texas Government Code, §2001.0225.
BCCA, Dynegy, ExxonMobil, Phillips 66, and REI stated that the proposed
rules did not include an adequate TIA as required under Texas Government Code, §2007.
The commenters stated that the TIA provision mandates that covered agencies
"take a 'hard look' at the private real property implications of the actions
they undertake...," according to the Office of the Attorney General,
The commenters stated that agencies must also comply with guidelines developed
by the Texas Attorney General when developing the TIA and that according to
these guidelines, agencies must carefully review governmental actions that
have a significant impact on the owner's economic interest. The commenters
stated that these guidelines include the statement: "Although a reduction
in property value alone may not be a 'taking,' a severe reduction in property
value often indicates a reduction or elimination of reasonably profitable
uses." (21 TexReg 392, January 12, 1996). The commenters stated that examples
of aspects of the rule proposal that could significantly impact private real
property in a manner that constitutes a taking include gas-fired compressor
engines and other point source NO
x
controls.
The commenters stated that the rule proposal preamble acknowledged that retrofitting
compressor engines to the level specified in the proposal (25 TexReg 8137
and 8291) is infeasible, and stated that the existing equipment, representing
a significant capital improvement at a number of industrial sites, would be
rendered unusable. The commenters stated that the 90% point source reduction
requirement is economically and technologically infeasible for a number of
existing sites, and that this requirement could cause a number of facilities
to shut down their operations, dramatically impacting the value of their real
property.
The commenters stated that the proposed rule preamble acknowledged that
some of the rules may "burden" private real property, but claimed an exemption
from performing a TIA based on the assertion that the proposal does not impose
a greater burden than necessary to advance a health and safety purpose and
that the proposal "reasonably" fulfills a federal mandate. (25 TexReg 8175,
8194, 8201, 8208, 8220, 8228, 8237, 8245, 8294, and 8295). The commenters
stated that the commission provided the public no basis to infer that a cost/benefit
analysis or a reasonableness determination was, in fact, performed as necessary
to support the TIA exemption claim because the preamble contains only the
bare assertions. The commenters asserted that the proposed rules will impose
a greater burden than is necessary, and are not reasonably taken to fulfill
a federal mandate. The commenters commented that according to the Attorney
General's guidelines, a full TIA was required to be completed with the proposal,
and that failure to perform a TIA could invalidate the rules.
The primary reason the commission determined that these rules did not constitute
a takings under Texas Government Code, Chapter 2007 is that it will not burden
private real property. These rules apply to non-road equipment which is not
real property or appurtenance thereto.
In its analysis, the commission also found that this rulemaking action
is exempt from Texas Government Code, Chapter 2007 under §2007.003(b)(4)
because it is reasonably taken to fulfill an obligation mandated by federal
law. The commission included elsewhere in this preamble its reasoned justification
for adopting this strategy and has explained why it is a necessary component
of the SIP which is federally mandated. This discussion, as well as the HGA
SIP which is being adopted concurrently, explains in detail that every rule
in the HGA SIP package is necessary and that none of the reductions in those
packages represent more than is necessary to bring the area into attainment
with the NAAQS. This rulemaking action therefore meets the requirements of §2007.003(b)(4).
For these reasons this rulemaking action not constitute a takings under Chapter
2007 and does not require additional analysis.
ExxonMobil, Phillips 66, and REI stated that the proposed rules did not
include adequate notice as required under Texas Government Code, §2002.024.
The commenters stated that §2001.024, requires adequate notice of a proposed
rule, including information about its public benefits and costs. The commenters
stated that adequate notice is essential for fairness as well as a meaningful
opportunity to comment on a proposed rule, and that courts have considered
notice "adequate" only if: interested persons can confront the agency's factual
suppositions and policy preconceptions; and the agency provides interested
parties the opportunity to challenge the underlying factual data relied upon
by the agency. The commenters asserted that in proposing the rules, the commission
failed to provide interested parties with sufficient information to constitute
adequate notice.
The commenters stated that the rule proposal preamble appears short of
adequate notice because the cost estimates were "dramatically underestimated."
The commenters stated that the commission published insufficient information
and analysis regarding costs and impacts.
The commenters also noted that the rule proposal preamble stated that "there
may be individual sources for which the equipment actual control costs are
higher than the ones identified in this cost note," and asserted that through
this statement the commission "acknowledged that its estimates may have been
low."
The commenters stated that it has identified a number of critical gaps
in the underlying factual data, methodology, and analysis in support of the
proposed rules. The commenters asserted that the proposal included insufficient
information and analysis regarding costs and impacts. The commenters asserted
that the commission has not adequately responded to requests for additional
information from stakeholders. The commenters stated that the following requests
for information included outstanding: information regarding the modeling of
emissions; information regarding the corrected emissions inventory database;
and information supporting the estimated costs of control. The commenters
stated that this information is necessary in order to comment effectively
on the proposed rules and that data gaps in the proposal hindered effective
comment.
The commission disagrees with the commenters and has made no change in
response to these comments. Texas Government Code, §2001.024 requires
that the notice of proposed rules must include certain information. Subsection
(a)(5) requires the notice to state the public benefits expected as a result
of the adoption of the proposed rules, and the probable economic cost to persons
required to comply with these rules. Adequate notice is essential for fairness
as well as a meaningful opportunity to comment on proposed rules.
United Loans, Inc. v. Pettijohn,
955 S.W.2d 649, 651 (Tex. App.-Austin
1997). To achieve the goal of encouraging meaningful public participation
in the formulation and adoption of rules by state agencies, the notice must
have sufficient information so that interested persons can determine whether
it is necessary for them to participate in order to protect their legal rights
and privileges. The proposed rules contained an analysis of information available
to the commission regarding the costs and benefits. The commission received
intelligent comments which were substantial in both number and in scope, regarding
the costs as well as the benefits. Therefore, the commission believes this
goal has been achieved and that the notice includes sufficient information
to constitute adequate notice. The purpose of the comment period is for the
public to provide the commission with information to say why they agree or
disagree.
To simply state that the proposal failed to provide sufficient information
does not provide the commission with sufficient information to propose changes
or alternative strategies. The commenters did not say how the notice was insufficient,
merely that it was insufficient. Nevertheless, the commission reviewed the
notice and determined that it is adequate. The commission response to comments
regarding costs of compliance with these rules are discussed in the FINAL
REGULATORY IMPACT ANALYSIS DETERMINATION section of this preamble and throughout
this ANALYSIS OF TESTIMONY. The commission is unaware of any requests for
additional information to which it was not completely responsive.
REI, BCCA, Dynegy, and ExxonMobil commented that the proposal did not have
a local employment impact statement.
The commission agrees with the commenters that the rules may affect a local
economy, however, does not agree that it is the responsibility of the commission
to provide the local employment impact analysis. The APA requires state agencies
to determine whether rules may affect a local economy before proposing the
rules for adoption. If the agency determines that proposed rules may affect
a local economy, the agency must send a copy of the proposed rules and other
information to the Texas Workforce Commission (Workforce Commission) before
the agency files notice of the proposed rules with the secretary of state.
The APA requires the Workforce Commission to prepare a local employment impact
statement for proposed rules, if a state agency requests the statement. The
commission determined that the proposed rules might affect a local economy,
and sent the proposed rule and other requested information to the Workforce
Commission. The commission received a letter from the Workforce Commission,
indicating that they did not have the ability to determine the potential local
employment impacts for the proposed rules.
Baker Botts commented that it generally supports the ongoing efforts by
the commission to develop a SIP that is technologically achievable, economically
reasonable, and legally approvable. Baker Botts, BCCA, Dynegy, ExxonMobil,
Harris County, Phillips 66, and an individual commented that the commission
should incorporate into the SIP a greater level of reductions from federally
preempted sources and stated that EPA-regulated sources account for about
40% of the NO
x
emissions in the HGA. REI commented
that federal NO
x
reductions should be fully incorporated.
The commenters stated that the EPA issued a number of regulations for some
federally preempted sources, such as land-based spark engines; marine, recreational,
and land-based diesel engines; aircraft and locomotive engines; well after
the FCAA deadlines, and that the EPA recently strengthened rules for on-road
and non-road vehicles and fuels, such as low sulfur gas and diesel, Tier II
motor vehicles, heavy-duty highway vehicle standards, and non-road Tier 2/Tier
3 heavy-duty engine standards. The commenters stated that delays in implementing
these rules have prompted the commission to propose technically and economically
infeasible emission reductions from sources in HGA that the state has no authority
to regulate to make up for the missing federal reductions. The commenters
stated that these delays have forced the commission to propose expensive regional
fuels and significant use restriction regulations. The commenters stated that
the commission and the EPA can ensure an equitable distribution of the compliance
burdens necessary to meet mandated air quality improvement in HGA only by
allowing the SIP to capture anticipated emission reductions from federally
preempted sources. Baker Botts noted that the EPA demonstrated a willingness
to assume responsibility for a portion of emissions reductions by creating
a process in Los Angeles called a "public consultative process," that would
resolve issues related to emissions from national and international sources,
and that the EPA has also provided flexibility in obtaining offsets by allowing
states to provide offsets to refiners based on emissions reductions that the
EPA projected would result from mobile sources using Tier II gasoline. Baker
Botts suggested that this same sort of prospective crediting should be used
to develop a more rational HGA SIP, and that the EPA should allow the commission
to claim credit in the SIP for the prospective emission reductions that will
result from implementation of the Tier II gasoline rule and from other federally
preempted sources. Finally, Baker Botts cited two cases in which the District
of Columbia Circuit Court approved the EPA flexibility with respect to statutory
deadlines under 42 USC when the EPA failed to meets its own deadlines, and
this failure was deemed to upset the balanced federal/state responsibilities
under 42 USC. ExxonMobil commented that it supported the commission and the
EPA crediting the HGA SIP with an additional 60 tpd of federally preempted
emission reductions that will occur over the next ten years. Harris County
commented that the commission should work with the EPA to accelerate the implementation
schedule for federally preempted emissions so that at least one-half of the
related emission reductions are achieved by 2007, and that as a part of this
process, the commission should delineate federal assignments detailing the
engine standards and emission reductions necessary to achieve real and sustainable
pollution reductions.
The commission agrees with the commenters that emission reductions from
federally preempted sources would provide benefits for the HGA SIP demonstration,
and the inability of the commission to regulate certain source categories
has necessitated the use of other ozone control strategies. However, the commission
understands that the EPA SIP approval process does not provide a mechanism
for credit for emission reductions that occur after the attainment date. The
commission understands that EPA is not currently considering accelerating
implementation schedules for existing federal rules. The commission is working
with the EPA to determine the availability of SIP credit for many non-traditional
control strategy mechanisms, like economic incentive programs and flexibility
for preempted source categories. Additionally, the commission is working with
the EPA to determine an appropriate federal contribution credit available
for the HGA SIP.
STATUTORY AUTHORITY
The amendments are adopted under TWC, §5.103, which authorizes the
commission to adopt rules necessary to carry out its powers and duties under
the TWC, and under the Texas Health and Safety Code, TCAA, §382.017,
which provides the commission the authority to adopt rules consistent with
the policy and purposes of the TCAA. The amendments are also adopted under
TCAA, §382.011, which authorizes the commission to control the quality
of the state's air; §382.012, which authorizes the commission to prepare
and develop a general, comprehensive plan for the control of the state's air; §382.019,
which authorizes the commission to adopt rules to control and reduce emissions
from engines used to propel land vehicles; and §382.039, which authorizes
the commission to develop and implement transportation programs and other
measures necessary to demonstrate attainment and protect the public from exposure
to hazardous air contaminants from motor vehicles.
This agency hereby certifies that the adoption has been reviewed
by legal counsel and found to be a valid exercise of the agency's legal authority.
Filed with the Office of
the Secretary of State on December 29, 2000.
TRD-200009082
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Effective date: January 18, 2001
Proposal publication date: August 25, 2000
For further information, please call: (512) 239-0348
30 TAC §114.452, §114.459
The Texas Natural Resource Conservation Commission (commission)
adopts new §114.452, Control Requirements; and §114.459, Affected
Counties and Compliance Dates. The commission adopts these revisions to add
new Division 6, Lawn Service Equipment Operating Restrictions, to Subchapter
I, Non-road Engines; Chapter 114, Control of Air Pollution from Motor Vehicles;
and to the associated state implementation plan (SIP). The commission adopts
these amendments to Chapter 114 and corresponding revisions to the SIP in
order to control ground-level ozone in the Houston/Galveston (HGA) ozone nonattainment
area. The revisions are one element of the control strategy for the HGA Post-1996
Rate-of-Progress (ROP)/Attainment Demonstration SIP. Sections 114.452 and
114.459 are adopted
with changes
to the proposed
text as published in the August 25, 2000 issue of the
Texas Register
(25 TexReg 8216).
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE ADOPTED RULES
The HGA ozone nonattainment area is classified as Severe-17 under the Federal
Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401
et seq.), and therefore is required to attain the one-hour ozone standard
of 0.12 parts per million (ppm) by November 15, 2007. In addition, 42 USC, §7502(a)(2),
requires attainment as expeditiously as practicable, and 42 USC, §7511a(d),
requires states to submit ozone attainment demonstration SIPs for severe ozone
nonattainment areas such as HGA. The HGA area, defined by Brazoria, Chambers,
Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has
been working to develop a demonstration of attainment in accordance with 42
USC, §7410. On January 4, 1995, the state submitted the first of its
Post-1996 SIP revisions for HGA.
The January 1995 SIP consisted of urban airshed model (UAM) modeling for
1988 and 1990 base-case episodes, adopted rules to achieve a 9% ROP reduction
in volatile organic compounds (VOC), and a commitment schedule for the remaining
ROP and attainment demonstration elements. At the same time, but in a separate
action, the State of Texas filed for the temporary nitrogen oxides (NO
Around the same time as the 1995 submittal, the EPA policy regarding SIP
elements and timelines went through changes. Two national programs in particular
resulted in changing deadlines and requirements. The first of these programs
was the Ozone Transport Assessment Group (OTAG). This group grew out of a
March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for
Air and Radiation, that allowed states to postpone completion of their attainment
demonstrations until an assessment of the role of transported ozone and precursors
had been completed for the eastern half of the nation, including the eastern
portion of Texas. Texas participated in this study, and it has been concluded
that Texas does not significantly contribute to ozone exceedances in the Northeastern
United States. The other major national initiative that has impacted the SIP
planning process is the revisions to the national ambient air quality standard
(NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing
the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996,
concurrent with the proposal of the standards, the EPA proposed an interim
implementation plan (IIP) that it believed would help areas like HGA transition
from the old to the new standard. In an attempt to avoid a significant delay
in planning activities, Texas began to follow this guidance, and readjusted
its modeling and SIP development timelines accordingly. When the new standard
was published, the EPA decided not to publish the IIP, and instead stated
that, for areas currently exceeding the one-hour ozone standard, that standard
would continue to apply until it is attained. The FCAA requires that HGA attain
the standard by November 15, 2007.
The EPA issued revised draft guidance for areas such as HGA that do not
attain the one-hour ozone standard. The commission adopted on May 6, 1998
and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained
the following elements in response to the EPA guidance: UAM modeling based
on emissions projected from a 1993 baseline out to the 2007 attainment date;
an estimate of the level of VOC and NO
x
reductions
necessary to achieve the one-hour ozone standard by 2007; a list of control
strategies that the state could implement to attain the one-hour ozone standard;
a schedule for completing the other required elements of the attainment demonstration;
a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the
EPA believed made the previous version of that SIP unapprovable; and evidence
that all measures and regulations required by the Subpart 2 of Title I of
the FCAA to control ozone and its precursors have been adopted and implemented,
or are on an expeditious schedule to be adopted and implemented.
In November 1998, the SIP revision submitted to the EPA in May 1998 became
complete by operation of law. However, the EPA stated that it could not approve
the SIP until specific control strategies were modeled in the attainment demonstration.
The EPA specified a submittal date of November 15, 1999 for this modeling.
In a letter to the EPA dated January 5, 1999, the state committed to model
two strategies showing attainment.
As the HGA modeling protocol evolved, the state eventually selected and
modeled seven basic modeling scenarios. As part of this process, a group of
HGA stakeholders worked closely with commission staff to identify local control
strategies for the modeling. Some of the scenarios for which the stakeholders
requested evaluation included options such as California-type fuel and vehicle
programs as well as an acceleration simulation mode equivalent motor vehicle
inspection and maintenance program. Other scenarios incorporated the estimated
reductions in emissions that were expected to be achieved throughout the modeling
domain as a result of the implementation of several voluntary and mandatory
state-wide programs adopted or planned independently of the SIP. It should
be made clear that the commission did not propose that any of these strategies
be included in the ultimate control strategy submitted to the EPA in 2000.
The need for and effectiveness of any controls which may be implemented outside
the HGA eight-county area will be evaluated on a county-by-county basis.
The SIP revision was adopted by the commission on October 27, 1999, submitted
to the EPA by November 15, 1999, and contained the following elements: photochemical
modeling of potential specific control strategies for attainment of the one-hour
ozone standard in the HGA area by the attainment date of November 15, 2007;
an analysis of seven specific modeling scenarios reflecting various combinations
of federal, state, and local controls in HGA (additional scenarios H1 and
H2 build upon Scenario VIf); identification of the level of reductions of
VOC and NO
x
necessary to attain the one-hour
ozone standard by 2007; a 2007 mobile source budget for transportation conformity;
identification of specific source categories which, if controlled, could result
in sufficient VOC and/or NO
x
reductions to attain
the standard; a schedule committing to submit by April 2000 an enforceable
commitment to conduct a mid-course review; and a schedule committing to submit
modeling and adopted rules in support of the attainment demonstration by December
2000.
The April 19, 2000 SIP revision for HGA contained the following enforceable
commitments by the state: to quantify the shortfall of NO
x
reductions needed for attainment; to list and quantify potential
control measures to meet the shortfall of NO
x
reductions needed for attainment; to adopt the majority of the necessary rules
for the HGA attainment demonstration by December 31, 2000, and to adopt the
rest of the shortfall rules as expeditiously as practical, but no later than
July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform
a mid- course review by May 1, 2004; and to perform modeling of mobile source
emissions using the EPA mobile source emissions model (MOBILE6), to revise
the on-road mobile source budget as needed, and to submit the revised budget
within 24 months of the model's release. In addition, if a conformity analysis
is to be performed between 12 months and 24 months after the MOBILE6 release,
the state will revise the motor vehicle emissions budget (MVEB) so that the
conformity analysis and the SIP MVEB are calculated on the same basis.
In order for the state to have an approvable attainment demonstration,
the EPA indicated that the state must adopt those strategies modeled in the
November 1999 submittal and then adopt sufficient controls to close the remaining
gap in NO
x
emissions. The modeling and other
analysis supporting these rules and the HGA SIP indicates a gap of approximately
91 tons per day (tpd) of NO
x
reductions is necessary
for an approvable attainment demonstration. The commission estimates that
this measure will achieve a minimum of 0.23 tpd delay of NO
x
until after noon. There will also be a 12.4 tpd delay in VOC emissions
until after noon. Because the emission of NO
x
and VOC, both precursors to the formation of ozone, will be delayed until
after noon, this delay will lead to a reduction in ozone that is equal to
approximately 4.6 tpd NO
x
reduced. These reductions
are a necessary measure to consider for closing the gap and successfully demonstrating
attainment.
The emission reduction requirements included as part of this SIP revision
represent substantial, intensive efforts on the part of stakeholder coalitions
in the HGA area. These coalitions, involving local governmental entities,
elected officials, environmental groups, industry, consultants, and the public,
as well as the commission and the EPA, worked diligently to identify and quantify
potential control strategy measures for the HGA attainment demonstration.
Local officials from the HGA area formally submitted a resolution to the commission,
requesting the inclusion of many specific emission reduction strategies.
This rule adoption is one element of the control strategy for the HGA SIP.
Adoption and implementation of this control strategy is necessary in order
for the HGA nonattainment area to comply with the requirements of the FCAA
and achieve attainment for ozone. Additional elements of the control strategy
for the HGA SIP are being adopted concurrently in this issue of the
The amount of NO
x
reductions required for
the area to attain the ozone NAAQS has been estimated by extensive use of
air quality grid modeling, which because of its scientific and statutory grounding,
is the chief policy tool for designing emission reduction strategies. The
FCAA, 42 USC, §7511a(c)(2), requires the use of photochemical grid modeling
for ozone nonattainment areas designated serious, severe, or extreme. The
modeling has been conducted with input from a technical oversight committee.
Commission staff have continued to improve the air quality modeling technology
and refine emission inventory data. Numerous emission control strategies were
considered in developing the modeling. Varying degrees of reductions from
point sources, on-road and non-road mobile sources, and area sources were
analyzed in multiple iterations of modeling, to test the effectiveness of
different NO
x
reductions. The attainment demonstration
modeling and other analysis submitted for public hearing and comment concurrently
with the HGA SIP show that a significant amount of NO
x
reductions practicably achievable are necessary from ozone control
strategies in order for the HGA nonattainment area to achieve the ozone NAAQS
by 2007, including reductions from surrounding counties included in the HGA
consolidated metropolitan statistical area (CMSA).
Additionally, reductions associated from the ozone control strategies that
will be implemented outside the HGA nonattainment area will benefit the HGA
nonattainment area. This is due to the regional nature of air pollution, the
contribution from mobile sources, and the economies of scale and associated
market advantages related to distribution networks for some strategies. At
the time the 1990 FCAA Amendments were enacted, the focus on controlling ozone
pollution was centered on local controls. However, for many years an ever
increasing number of air quality professionals have concluded that ozone is
a regional problem requiring regional strategies in addition to local control
programs. As nonattainment areas across the United States prepared attainment
demonstration SIPs in response to the 1990 FCAA Amendments, several areas
found that modeling attainment was made much more difficult, if not impossible,
due to high ozone and ozone precursor levels entering from the boundaries
of their respective modeling domains, commonly called transport. Recent science
indicates that regional approaches may provide improved control of ozone air
pollution.
The current SIP revision contains rules, enforceable commitments, photochemical
modeling analyses, and calculation of the remaining NO
x
reductions required to reach attainment (gap calculation) in support
of the HGA ozone attainment demonstration. In addition, this SIP contains
Post-1999 ROP plans for the milestone years 2002 and 2005, and for the attainment
year 2007. The SIP also contains enforceable commitments to implement further
measures, if needed, in support of the HGA attainment demonstration, as well
as a commitment to perform and submit a mid- course review.
The HGA ozone nonattainment area will need to ultimately reduce NO
The purpose of these rules is to establish a restriction on the use of
handheld and non-handheld spark-ignition engines that operate at or below
25 horsepower (hp), or 19 kilowatts. This air pollution control strategy would
delay the emissions of NO
x
from these engines
until later in the day, thus limiting ozone production. This control strategy
is necessary for the HGA nonattainment area to be able to demonstrate attainment
with the NAAQS for ozone.
These rules would implement an operating-use restriction program requiring
that the handheld and non-handheld spark-ignition engines, rated at 25 hp
and below, be restricted from use by commercial operators between the hours
of 6:00 a.m. and noon, April 1 through October 31. The affected handheld equipment
includes, but is not limited to, trimmers, edgers, chain saws, leaf blowers/vacuums,
and shredders. Non-handheld lawn and garden equipment includes such devices
as walk-behind lawnmowers, lawn tractors, tillers, and small generators. The
affected area would include the following counties within the HGA nonattainment
area: Brazoria, Fort Bend, Galveston, Harris, and Montgomery. Based on estimated
population, estimated population growth, and emissions estimates developed
using EPA-approved methodologies, the commission believes it is not necessary
to include Chambers, Liberty, and Waller Counties in the adopted rules. This
issue is discussed in greater detail in the ANALYSIS OF TESTIMONY section
of this preamble. The effective date would be April 1, 2005.
The intent of these rules is to limit the use of handheld and non-handheld
spark-ignition lawn and garden service equipment that operate at or below
25 hp between the hours of 6:00 a.m. and noon. Other lawn and garden service
work not requiring the use of handheld and non-handheld spark-ignition lawn
and garden service equipment remains unrestricted under these rules. That
is, electric or man- powered lawn equipment may be used. It should be noted
however that the regulated types of lawn and garden service equipment are
banned from use by commercial operators during the hours specified regardless
of how they are being used.
The amount of NO
x
shifted will total 0.23
tpd. The non-road mobile source category is one of the few sources of ozone-causing
emissions that are not currently regulated under rules adopted by the commission.
Federal controls on handheld lawn and garden service equipment such as cleaner-burning
engines have been adopted and been in effect since 1997. More stringent standards
will be phased in beginning with the 2002 model year.
The California Air Resources Board (CARB) stated that "using a commercial
chain saw - powered by a two-stroke engine - for two hours produces the same
amount of smog-forming hydrocarbon emissions as driving ten 1996 cars about
250 miles each." By shifting the hours of use for handheld and non-handheld
spark-ignition lawn and garden service equipment until after noon, NO
The commission solicited comment on additional flexibilities relating to
rule content and implementation which have not been addressed in this or other
concurrent rulemakings. These flexibilities may be available for both mobile
and stationary sources. Additional flexibilities may also be achieved through
innovative and/or emerging technology which may become available in the future.
Additional sources of funds for incentive programs may become available to
substitute for some of the measures considered here.
The commission also solicited comments on alternative applications of this
rule including: innovative uses of technology, such as incentives to use ultra-low
emission engines; alternative use restrictions, such as restricting use to
every tenth day; and alternative restrictions on commercial use versus residential
use, such as limiting the application of the rule to commercial services (which
could be at residential property) or activities at commercial (versus residential)
properties.
SECTION BY SECTION DISCUSSION
The new Division 6 is adopted regarding operating restrictions for commercial
operators using lawn and garden service equipment powered by spark-ignition
engines 25 hp or below.
The new §114.452(a) establishes operating restrictions for commercial
operators' using lawn and garden service equipment. These rules restrict the
operation by commercial operators of all handheld or non-handheld spark-ignition
equipment 25 hp and below, between the hours of 6:00 a.m. and noon, during
the time period between April 1 and October 31, except as specified in §114.452(b)
and (c).
The new §114.452(b)(1) and (2) state that the use of spark-ignition
engines under 25 hp are exempt from the requirements of these rules when used
at a domestic residence by the owner of, or a resident at, that domestic residence,
or when used by a non-commercial operator. New §114.452(b)(3) exempts
any equipment used exclusively for emergency operations to protect human health
and safety or the environment, including equipment being used in the repair
of facilities, devices, systems, or infrastructure that have failed, or are
in danger of failing, in order to prevent immediate harm to public health,
safety, or the environment.
The new §114.452(c) states that commercial operators or persons who
submit an approved emissions reduction plan are exempt from operating hour
restrictions in 2005. The commission is requiring submission of the plans
by May 31, 2003, to allow sufficient time to review and quantify the collective
emission reductions the plans propose. The plans will be approved by the executive
director and the EPA by May 31, 2004. The commission is requiring submission
of the emissions reduction plans two years prior to the compliance date to
allow adequate time for review of the plans, both by the commission and the
EPA, and to allow the commission to ensure that the collective emission reductions
achieved by the plans are equivalent to the ozone reductions achieved by implementation
of the rules. Approved plans would allow commercial operators to operate during
the restricted hours. In order to be approved, a plan must demonstrate NO
The new §114.452(d) states that a commercial operator is defined as
any person who receives payment or compensation in exchange for operating
lawn and garden service equipment powered by spark-ignition engines of 25
hp where the payment or compensation is required to be reported as income
by the United States Internal Revenue Code. Generally speaking, this is any
person who earns more than $400 a year using the aforementioned equipment.
Furthermore, this term also includes any employees or contractors of any person
as defined in the Texas Clean Air Act (TCAA), §382.003(10). This means
that those entities like government bodies and/or businesses that sustain
their own workforce to provide lawn and garden services are not exempt from
these rules.
The new §114.459 specifies when the rule becomes effective (i.e.,
2005), and the counties which are subject to the new requirements. The affected
counties include Brazoria, Fort Bend, Galveston, Harris, and Montgomery Counties.
Based on estimated population, estimated population growth, and estimated
emissions developed using EPA-approved methodologies, the commission believes
it is not necessary to include Chambers, Liberty, and Waller Counties in the
adopted rule. This issue is discussed in greater detail in the ANALYSIS OF
TESTIMONY section of this preamble.
FINAL REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed this rulemaking action in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225, and determined
that the rulemaking does not meet the definition of a "major environmental
rule" as defined in that statute. "Major environmental rule" means a rule
the specific intent of which is to protect the environment or reduce risks
to human health from environmental exposure and that may adversely affect
in a material way the economy, a sector of the economy, productivity, competition,
jobs, the environment, or the public health and safety of the state or a sector
of the state.
These adopted rules do not meet any of the four applicability criteria
for requiring a regulatory analysis of "major environmental rule" as defined
in the Texas Government Code. Section 2001.0225 applies only to a major environmental
rule the result of which is to: 1) exceed a standard set by federal law, unless
the rule is specifically required by state law; 2) exceed an express requirement
of state law, unless the rule is specifically required by federal law; 3)
exceed a requirement of a delegation agreement or contract between the state
and an agency or representative of the federal government to implement a state
and federal program; or 4) adopt a rule solely under the general powers of
the agency instead of under a specific state law.
As discussed earlier in this preamble, this rule adoption is one element
of the control strategy for the HGA SIP. Adoption and implementation of this
control strategy is necessary in order for the HGA nonattainment area to comply
with the requirements of the FCAA and achieve attainment for ozone. Additional
elements of the control strategy for the HGA SIP are being adopted concurrently
in this issue of the
Texas Register
, or were
included in the HGA SIP considered by the commission on December 6, 2000,
and planned to be submitted to EPA by December 31, 2000.
These rules in Chapter 114 are intended to protect the environment or reduce
risks to human health from environmental exposure to ozone and, although no
estimates of cost were available to the commission at the time of proposal
of the rules, the commission does not believe work delays could affect a sector
of the economy in an adverse, material way. These rules are intended to implement
an operating-use restriction program requiring that lawn and garden service
equipment powered by spark- ignition engines, 25 hp or below utilized by commercial
operators, or for uses not exempt under §114.452(b), will be restricted
from use between the hours of 6:00 a.m. and noon, April 1 through October
31. This program is part of the strategy to reduce the formation of ozone
by delaying NO
x
emissions from lawn and garden
equipment until later in the day when optimum conditions for the formation
of ozone no longer exist. The program was developed for the HGA ozone nonattainment
area to be able to demonstrate attainment with the ozone NAAQS. The commission
does not believe that the businesses that provide lawn and garden services
comprise a sector of the economy, nor does the commission believe that the
rules will adversely affect in a material way, the economy, productivity,
competition, jobs, the environment, or the public health and safety of the
state or a sector of the state.
These rules do not exceed an express standard set by federal law, since
they implement requirements of the FCAA. Under 42 USC, §7410, states
are required to adopt a SIP which provides for "implementation, maintenance,
and enforcement" of the primary NAAQS in each air quality control region of
the state. These rules were specifically developed as part of an overall control
strategy to meet the ozone NAAQS set by the EPA under 42 USC, §7409.
While 42 USC, §7410, does not require specific programs, methods, or
reductions in order to meet the standard, state SIPs must include "enforceable
emission limitations and other control measures, means or techniques (including
economic incentives such as fees, marketable permits, and auctions of emissions
rights), as well as schedules and timetables for compliance as may be necessary
or appropriate to meet the applicable requirements of this chapter," (meaning
FCAA, Chapter 85, Air Pollution Prevention and Control). It is true that the
FCAA does require some specific measures for SIP purposes, such as the inspection
and maintenance program, but those programs are the exception, not the rule,
in the SIP structure of the FCAA. The provisions of the FCAA recognize that
states are in the best position to determine what programs and controls are
necessary or appropriate in order to meet the NAAQS. This flexibility allows
states, affected industry, and the public, to collaborate on the best methods
for attaining the NAAQS for the specific regions in the state. Even though
the FCAA allows states to develop their own programs, this flexibility does
not relieve a state from developing a program that meets the requirements
of 42 USC, §7410. In order to avoid federal sanctions, states are not
free to ignore the requirements of 42 USC, §7410, and must develop programs
to assure that the nonattainment areas of the state will be brought into attainment
on schedule. Thus, while specific measures are not prescribed, both a plan
and emission reductions are required to assure that the nonattainment areas
of the state will be able to meet the attainment deadlines set by the FCAA.
The EPA has provided the criteria for both the submission and evaluation of
attainment demonstrations developed by states to comply with the FCAA. This
criteria requires states to provide, in addition to other information, photochemical
modeling and an analysis of specific emission reduction strategies necessary
to attain the NAAQS. The commission's photochemical modeling and other analysis
indicate that substantial emission reductions from both mobile and point source
categories are necessary in order to demonstrate attainment. In this case,
this rulemaking is intended to achieve reductions in ozone precursor emissions
in the HGA nonattainment area. Specifically, as noted elsewhere in this rule
preamble, the emission reductions associated with these rules are a necessary
element of the attainment demonstration required by the FCAA.
In addition, 42 USC, §7502(a)(2), requires attainment as expeditiously
as practicable, and 42 USC, §7511a(d), requires states to submit ozone
attainment demonstration SIPs for severe ozone nonattainment areas such as
HGA. By policy, the EPA requires photochemical grid modeling to demonstrate
whether the 42 USC, §7511a(f), NO
x
measures
would contribute to ozone attainment. The commission has performed photochemical
grid modeling which predicts that NO
x
emission
reductions, such as those required by these rules, will result in reductions
in ozone formation in the HGA ozone nonattainment area and help bring HGA
into compliance with the air quality standards established under federal law
as NAAQS for ozone. The 42 USC, §7511a(f), exemption from NO
x
measures for HGA expired on December 31, 1997. The expiration of
the exemption under 42 USC, §7511a(f), was based on the finding that
NO
x
reductions in HGA are necessary for attainment
of the ozone standard. Therefore, the adopted amendments are necessary components
of and consistent with the ozone attainment demonstration SIP for HGA, required
by 42 USC, §7410.
During the 75th Legislative Session, Senate Bill (SB) 633 amended the Texas
Government Code to require agencies to perform a regulatory impact analysis
(RIA) of certain rules. The intent of SB 633 was to require agencies to conduct
an RIA of extraordinary rules. With the understanding that this requirement
would seldom apply, the commission provided a cost estimate for SB 633 that
concluded "based on an assessment of rules adopted by the agency in the past,
it is not anticipated that the bill will have significant fiscal implications
for the agency due to its limited application." The commission also noted
that the number of rules that would require assessment under the provisions
of the bill was not large. This conclusion was based, in part, on the criteria
set forth in the bill that exempted proposed rules from the full analysis
unless the rule was a major environmental rule that exceeds a federal law.
As discussed earlier in this preamble, the FCAA does not require specific
programs, methods, or reductions in order to meet the NAAQS; thus, states
must develop programs for each nonattainment area to ensure that area will
meet the attainment deadlines. Because of the ongoing need to address nonattainment
issues, the commission routinely proposes and adopts SIP rules. The legislature
is presumed to understand this federal scheme. If each rule proposed for inclusion
in the SIP was considered to be a major environmental rule that exceeds federal
law, then every SIP rule would require the full RIA contemplated by SB 633.
This conclusion is inconsistent with the conclusions reached by the commission
in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal
notes. Since the legislature is presumed to understand the fiscal impacts
of the bills it passes, and that presumption is based on information provided
by state agencies and the LBB, the commission believes that the intent of
SB 633 was only to require the full RIA for rules that are extraordinary in
nature. While the SIP rules will have a broad impact, that impact is no greater
than is necessary or appropriate to meet the requirements of the FCAA.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
It is presumed that "when an agency interpretation is in effect at the time
the legislature amends the laws without making substantial change in the statute,
the legislature is deemed to have accepted the agency's interpretation."
The commission's interpretation of the RIA requirements is also supported
by a change made to the Texas Administrative Procedure Act (APA) by the legislature
in 1999. In an attempt to limit the number of rule challenges based upon APA
requirements, the legislature clarified that state agencies are required to
meet these sections of the APA against the standard of "substantial compliance."
Texas Government Code, §2001.035. The legislature specifically identified
Texas Government Code, §2001.0225 as falling under this standard. The
commission has substantially complied with the requirements of §2001.0225.
Therefore, in addition to not exceeding an express standard set by federal
law, these rules do not exceed state requirements, and are not adopted solely
under the general powers of the agency because the provisions of the TCAA, §§382.011,
382.012, 382.017, 382.019, and 382.039 authorize the commission to implement
a plan for the control of the state's air quality, including measures necessary
to meet federal requirements. The remaining applicability criteria, pertaining
to exceeding a delegation agreement or contract between the state and the
federal government does not apply. Thus, the commission is not required to
conduct a regulatory analysis as provided in Texas Government Code, §2001.0225.
Comments received during the comment period regarding the draft RIA are
addressed in the ANALYSIS OF TESTIMONY section of this preamble.
TAKINGS IMPACT ASSESSMENT
The commission evaluated this rulemaking action and performed an analysis
of whether the rules are subject to Texas Government Code, Chapter 2007. The
following is a summary of that analysis. The specific purpose of these amendments
is to develop a new attainment demonstration SIP for the ozone NAAQS for HGA
by adopting a lawn and garden service equipment operating-use limitation on
engines 25 hp and below to delay NO
x
emissions
that lead to high levels of ground- level ozone production. This rulemaking
action will act as an air pollution control strategy to shift NO
x
emissions necessary for the HGA ozone nonattainment area to be able
to demonstrate attainment with the ozone NAAQS. Adoption and enforcement of
the rules will not burden private, real property as the rules only regulate
handheld and non-handheld spark-ignition lawn and garden equipment rated at
25 hp or less.
Texas Government Code, §2007.003(b)(4), provides that Chapter 2007
does not apply to these adopted rules since they are reasonably taken to fulfill
an obligation mandated by federal law. The requirements within this rulemaking
were developed in order to meet the NAAQS for ozone set by the EPA under 42
USC, §7409. States are primarily responsible for ensuring attainment
and maintenance of NAAQS once the EPA has established them. Under 42 USC, §7410,
and related provisions, states must submit, for approval by the EPA, SIPs
that provide for the attainment and maintenance of NAAQS through control programs
directed to sources of the pollutants involved. Therefore, the purpose of
this rulemaking is to implement a lawn and garden service equipment operating
use limitation that is necessary for the HGA nonattainment area to meet the
air quality standards established under federal law as NAAQS. Consequently,
these rules meet the exception under §2007.003(b)(4).
In addition, Texas Government Code, §2007.003(b)(13), states that
Chapter 2007 does not apply to an action that: 1) is taken in response to
a real and substantial threat to public health and safety; 2) is designed
to significantly advance the health and safety purpose; and 3) does not impose
a greater burden than is necessary to achieve the health and safety purpose.
Although the rule revisions do not directly prevent a nuisance or prevent
an immediate threat to life or property, they do prevent a real and substantial
threat to public health and safety and significantly advance the health and
safety purpose. This action is taken in response to the HGA area exceeding
the NAAQS for ground-level ozone, which adversely affects public health, primarily
through irritation of the lungs. The action significantly advances the health
and safety purpose by reducing ambient VOC and ozone levels in HGA. Consequently,
these rules meet the exemption in §2007.003(b)(13).
The commission has included elsewhere in this preamble its reasoned justification
for adopting this strategy and has explained why it is a necessary component
of the SIP, which is federally mandated. This discussion, as well as the HGA
SIP which is being adopted concurrently, explain in detail that every rule
in the HGA SIP package is necessary and that none of the reductions in those
packages represent more than is necessary to bring the area into attainment
with the NAAQS. For these reasons the rules do not constitute a takings under
Chapter 2007 and do not require additional analysis. Comments received during
the comment period regarding the takings impact assessment (TIA) are addressed
in the ANALYSIS OF TESTIMONY section of this preamble.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that this rulemaking action relates to an action
or actions subject to the Texas Coastal Management Program (CMP) in accordance
with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources
Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter
281, Subchapter B, concerning Consistency with the CMP. As required by §281.45(a)(3)
and 31 TAC §505.11(b)(2), relating to actions and rules subject to the
CMP, commission rules governing air pollutant emissions must be consistent
with the applicable goals and policies of the CMP. The commission reviewed
this action for consistency with the CMP goals and policies in accordance
with the rules of the Coastal Coordination Council, and determined that the
action is consistent with the applicable CMP goals and policies. The CMP goal
applicable to this rulemaking action is the goal to protect, preserve, and
enhance the diversity, quality, quantity, functions, and values of coastal
natural resource areas (31 TAC §501.12(1)). No new sources of air contaminants
will be authorized and NO
x
air emissions will
be reduced as a result of these rules. The CMP policy applicable to this rulemaking
action is the policy that commission rules comply with regulations in 40 Code
of Federal Regulations (CFR), to protect and enhance air quality in the coastal
area (31 TAC §501.14(q)). This rulemaking action complies with 40 CFR
50, National Primary and Secondary Ambient Air Quality Standards, and 40 CFR
51, Requirements for Preparation, Adoption, and Submittal Of Implementation
Plans. Therefore, in compliance with 31 TAC §505.22(e), this rulemaking
action is consistent with CMP goals and policies.
The commission solicited comments on the consistency of the proposed rules
with the CMP during the public comment period. No comments were received during
the comment period regarding the CMP.
HEARINGS AND COMMENTERS
The commission held public hearings on this proposal at the following locations:
September 18, 2000, in Conroe and Lake Jackson; September 19, 2000 in Houston
(two hearings); September 20, 2000, in Katy and Pasadena; September 21, 2000,
in Beaumont, Amarillo, and Texas City; September 22, 2000, in Dayton, El Paso,
and Arlington; and September 25, 2000, in Austin and Corpus Christi. The comment
period closed at 5:00 p.m. on September 25, 2000.
The number of commenters who provided oral testimony and/or submitted written
testimony is 341. The following persons generally supported the proposal:
British Petroleum-Amoco (BP) and 13 individuals. The following persons generally
opposed the proposal: Liberty County EMS, Montgomery County Soil and Water
Conservation, State Representative John Culberson, and 30 individuals. The
following persons suggested changes to the proposal as stated in the ANALYSIS
OF TESTIMONY section of this preamble: AAA Asphalt Paving Inc. (AAA), Air
Cooled Engine Co. (ACEC), Amarillo Outdoor Power Equipment (AOPE), Baker
Botts LLP (Baker Botts), Bell Janitorial (Bell), Bio Energy Landscape &
Maintenance (Bio Energy), Business Coalition for Clean Air (BCCA), Citizens
for a Better Environment (CBE), City of Beasley (Beasley), City of Galveston
Public Works, City of Houston Mayor Brown, City of La Porte (La Porte), City
of Missouri City (Missouri City), City of Simonton (Simonton), City of Spring
Valley (Spring Valley), Clean Air Partnership (CAP), Cornelius Nurseries,
Inc. (Cornelius), Dayton Area Chamber of Commerce/Dayton Pipe Company (DACC/Dayton
Pipe), Engine Education and Training Council (EETC), Engine Warehouse Inc.
(EWI), Environmental Defense (ED), Excalibur Construction, Inc. (Excalibur),
ExxonMobil Corporation (ExxonMobil), Frazier Lawn Service, Inc. (Frazier),
Friendly Robotics, Galveston- Houston Association for Smog Prevention (GHASP),
Grandparents of East Harris County (GEHC), Greenscape, HARC Center for Global
Studies (HARC CGS), Harris County Judge Robert Eckels, Harris Landscape, The
Hispanic Community of Texas Citizens for a Solid Economy (TCSE-HC), Houston-Galveston
Metropolitan Planning Organization's Transportation Policy Council (Houston
MPO), Johnson Saw & Lawnmower Sales & Service (Johnson), League of
Women Voters of Texas (LWV-TX), Lynn's Landscaping, Inc. (Lynn's), Mayor
Louise Richman - City of Spring Valley, Houston Metropolitan Transit Authority
(Metro), Montgomery County (Montgomery Co.), Mothers for Clean Air (MCA),
Mustang Mowing and Landscape Service (Mustang Mowing), National Aeronautics
and Space Administration (NASA), Onalaska Equipment Rental and Repair, L.L.C.
(Onalaska), Outdoor Power Equipment Institute (OPEI), Pampered Lawns, Pate
and Pate Enterprises, Inc. (Pate & Pate), Personal Expressions Landscaping,
Inc. (Personal Expressions), Phillips 66 Company (Phillips 66), Portable Power
Equipment Manufacturers Association (PPEMA), Poulan Weedeater (Poulan), Public
Citizen, Regional Air Quality Consensus Group (RAQCG), Ray's Nursery (Ray's),
Reliant Energy, Inc. (REI), Rental Distributing Co. (RDC), Service Dealers
Association (TSDA), Sierra Club Galveston Region (Sierra-Galveston), Sierra
Club Houston Regional Group (Sierra-Houston), Small Business United of Texas
(SBU Texas), Society of St. Vincent de Paul (SVP), State Representative Robert
Talton, TNRCC Public Interest Counsel (PIC), Texas Association of Builders
(TAB), Texas Citizens for a Sound Economy (CSE), Texas Department of Transportation
(TxDOT), Texas Lawn and Landscape, Texas Nursery & Landscape Association
(TNLA), Tropical Landscape Services, Inc. (TLS), EPA, Wakefield Landscape
Service (Wakefield), Wesley Community Center, and 224 individuals. ExxonMobil,
Phillips 66 and REI supported the comments submitted by the BCCA; therefore,
references to BCCA will include references to these commenters. Lynn's, TLS,
and Cornelius Nurseries supported the comments of TNLA, therefore, references
to TNLA will include references to these commenters.
ANALYSIS OF TESTIMONY
BP and thirteen individuals commented that they supported the rules as
proposed. Liberty County EMS, Montgomery County Soil and Water Conservation,
State Representative John Culberson, and 30 individuals commented that they
opposed the rule as proposed.
Two individuals expressed support for limiting the lawn mowing ban to commercial
users only. Public Citizen and one individual commented that the rule should
apply to both commercial entities and individuals. TNLA, Harris Landscape,
Lynn's, AAA, Bell, Mustang Mowing, and two individuals commented that this
rule should not be applied to commercial lawn and garden companies. One individual
commented that individuals should be exempted from this rule.
The rule has been revised in response to these comments. The adopted rule
exempts any use at a domestic residence by the owner of, or a resident at,
that domestic residence or any use by a non- commercial operator. The rule
also exempts any use that is exclusively for emergency operations to protect
human health and safety or the environment, including equipment being used
in the repair of facilities, devices, systems, or infrastructure that have
failed, or are in danger of failing, in order to prevent immediate harm to
public health, safety, or the environment. The commission made this change
in the adopted rule to reduce the effect of the rule on individual home or
property owners while maintaining a level of ozone reduction that allows the
HGA area to demonstrate attainment of the ozone standard. The emission inventory
maintained by the commission indicates that commercial operators are the source
of the majority of weekday emissions from this type of equipment. The rule
has a new definition of commercial operator. A commercial operator is defined
as any person who receives payment or compensation in exchange for operating
lawn and garden service equipment powered by spark-ignition engines of 25
hp or below where the payment or compensation is required to be reported as
income by the United States Internal Revenue Code. This term also includes
any employees or contractors of any person as defined in the TCAA, §382.003(10).
This term is intended to cover lawn and garden service companies. The term
also references the definition of "person" from the TCAA in order to include,
for example, any employees or contractors of governmental entities, or corporations,
that might employ or hire their own lawn and garden service staff.
The adopted rule does allow commercial operators who submit an emissions
reduction plan by May 31, 2003, (which is approved by the executive director
and the EPA no later than May 31, 2004) to be exempt from operating hour restrictions
upon implementation of these rules in 2005. Thus, they would be permitted
to operate during the restricted hours. The executive director may allow plans
to be submitted after May 31, 2003. In any event, a plan must be approved
prior to the use of that plan for compliance with the requirements of this
division. In order to be approved, the plan must demonstrate NO
x
and VOC reductions equivalent to those required by the rules being
requested for exemption, and must contain adequate enforcement provisions.
Two individuals stated that any proposal which relies solely on the use
of new technology to lower pollution will not work. One individual commented
that the commission should not implement rules that are not based on proven
technologies.
This rule does not call for the use of new or unproven technology. The
purpose of the rule is to prohibit the use of lawn and garden equipment powered
by small, spark-ignition engines 25 hp and below from 6:00 a.m. to 12:00 p.m.
from April 1 to October 31 of each year except for domestic use and emergency
operations. The concept of shifting emissions until the afternoon has been
demonstrated to provide benefits in reducing ozone formation.
Dayton Pipe commented that Liberty County should be excluded from the HGA
SIP stating that Liberty County does not contribute to Houston's ozone problem.
An individual opposed implementation of the rules in Chambers and Liberty
Counties. Montgomery County asked to be excluded from the proposed air pollution
measures on the basis that doing so would not make any measurable difference
in the Houston ozone problem.
The FCAA Amendments of 1990 provided new requirements for areas that had
not attained the NAAQS for ozone, carbon monoxide, particulate matter, sulfur
dioxide, nitrogen dioxide, and lead, and new requirements for SIPs in general.
The EPA was authorized to designate areas failing to meet the NAAQS for ozone
as nonattainment and to classify them according to severity. Section 107(d)(4)(A)(iv)
of the FCAA mandated that areas designated as serious, severe, or extreme
for ozone that were within a metropolitan statistical area (MSA) or CMSA must
have boundaries that include the entire MSA or CMSA. This requirement is supported
by the legislative history for the FCAA Amendments in Senate Report No. 101
- 228, page 3399, "Because ozone is not a local phenomenon but is formed and
transported over hundreds of miles and several days, localized control strategies
will not be effective in reducing ozone levels. The bill, thus, expands the
size of areas that are defined as ozone nonattainment areas to assure that
controls are implemented in an area wide enough to address the problem." The
FCAA Amendments did provide the ability to exclude portions of the entire
MSA or CMSA prior to designation, if the state conducted a study that the
EPA agreed proved that the geographic portion did not contribute significantly
to violation of the NAAQS.
Redesignation has not occurred for any portion of the HGA nonattainment
area, and is not currently being considered. For existing areas currently
included within a nonattainment area, the specific area must be redesignated
as attainment to be removed from a nonattainment area. FCAA, §107(d)(3),
provides that the EPA may not redesignate a nonattainment area, or a portion
thereof, to attainment unless several criteria are met, which include: a determination
that the area has attained the NAAQS; there is a fully approved SIP for the
area; there is a determination that the improvement in air quality is due
to permanent and enforceable reductions in emissions; there is an approved
maintenance plan for the area; and the state has met all requirements for
the area under FCAA, §110 and Part D.
However, even if a specific area within the HGA nonattainment area was
redesignated by the EPA as attainment for ozone, reductions associated from
all adopted ozone control strategies would still be necessary because of the
requirements of FCAA, §107(d)(3) and §175A, which require maintenance
plans for all redesignated areas. The maintenance plan must include the measures
specified in §107(d)(3) and any additional measures that are necessary
to ensure that the area continues to be in attainment with the NAAQS for ten
years after the redesignation. Eight years after the redesignation, the state
is required to submit an additional revision to the SIP for maintaining the
NAAQS for ten years after the end of the first ten-year period.
Additionally, reductions associated from the ozone control strategies that
will be implemented outside the HGA nonattainment area will benefit the HGA
nonattainment area. This is due to the regional nature of air pollution, the
contribution from mobile sources, and the economies of scale and associated
market advantages related to distribution networks for some strategies.
At the time the 1990 FCAA Amendments were enacted, the focus on controlling
ozone pollution was centered on local controls. However, for many years an
ever increasing number of air quality professionals have concluded that ozone
is a regional problem requiring regional strategies in addition to local control
programs. As nonattainment areas across the United States prepared attainment
demonstration SIPs in response to the 1990 FCAA Amendments, several areas
found that modeling attainment was made much more difficult, if not impossible,
due to high ozone and ozone precursor levels entering from the boundaries
of their respective modeling domains, commonly called transport. Recent science
indicates that regional approaches may provide improved control of ozone air
pollution.
The commission has conducted air quality modeling and upper air monitoring
that found regional air pollution should be considered when studying air quality
in the Texas ozone nonattainment areas. This work is supported by research
conducted by OTAG, the most comprehensive attempt ever undertaken to understand
and quantify the transport of ozone. Both the commission and the OTAG study
point to the need to take a regional approach to controlling air pollutants.
The commission continues to believe that, in most cases, the most effective
method of achieving attainment in the HGA nonattainment area is the implementation
of controls and strategies throughout the nonattainment area. Much of the
HGA control strategy is based on this concept. However, provisions of the
FCAA recognize that states are in the best position to determine what programs
and controls are necessary or appropriate in order to meet the NAAQS. This
flexibility allows states, affected industry, and the public, to collaborate
on the best methods for attaining the NAAQS for the specific areas of the
state. Because of this flexibility, the commission can determine where emission
reduction measures are most needed and where emission reduction measures will
be most effective in order to demonstrate attainment. Based on estimated population,
estimated population growth, and estimated emissions developed using EPA-approved
methodologies, the commission has concluded that the sum of the 2007 projected
emissions from lawn and garden service equipment in Chambers, Liberty, and
Waller Counties is less than 3% of the total lawn and garden service equipment
projected emissions in the eight-county area. The effect of shifting lawn
and garden service equipment emissions in these three counties has been modeled,
therefore the commission believes that including these counties in the adopted
rule will have practically no beneficial impact on peak ozone levels. Further,
these three counties are primarily rural in nature thus, the commission believes
that lawn and garden service equipment emissions are more widely dispersed
geographically and are unlikely to significantly influence the urban ozone
plume. The commission does not, however, believe it is appropriate to exclude
Montgomery County.
Based on the January 1, 2000 population estimates compiled by the Texas
State Data Center, the population of Chambers County is 26,409; Waller County
is 29,208; and Liberty County is 68,687, for a total of 124,304. The estimated
population of the remaining counties in the HGA nonattainment area is Brazoria,
236,372; Galveston, 249,898; Montgomery, 295,263; Fort Bend, 356,555; and
Harris, 3,275,630, for a total of 4,413,718. The total estimated population
of the entire HGA nonattainment area is 4,538,022. Thus, the estimated population
of Liberty, Chambers, and Waller Counties is 2.74% of the population in the
HGA nonattainment area.
The total emissions from all of the HGA nonattainment counties for lawn
and garden service equipment is 1.16 tpd of NO
x
and 41.2 tpd of VOC. The estimated actual emissions from lawn and garden service
equipment for Liberty County is 0.0 tpd of NO
x
and 0.548 tpd of VOC; for Chambers County it is 0.0 tpd of NO
x
and 0.235 tpd of VOC; and for Waller County it is 0.0 tpd of NO
The same is not true, however, with respect to Montgomery County which
the commission believes should be retained in the adopted rule. Based on estimated
population, estimated population growth, and emissions estimates developed
using EPA-approved methodologies, the commission concluded that the sum of
the 2007 projected emissions from lawn and garden service equipment in Montgomery
County is 11.8% of the NO
x
and 13.6% of the VOC
of the total lawn and garden service equipment projected emissions in the
eight-county area. The effect of shifting lawn and garden service equipment
emissions in this county has been modeled, therefore the commission believes
that retaining Montgomery County in the adopted rule will have a measurable,
beneficial impact on peak ozone levels. Montgomery County is not primarily
rural in nature, thus lawn and garden service equipment emissions are not
as widely dispersed geographically as those same emissions are in Chambers,
Liberty, and Waller Counties, and are likely to influence the urban ozone
plume. Based on data compiled by the Texas State Data Center, Montgomery County
is the third largest county in the HGA nonattainment area with an estimated
population of 295,263, or about 6.51% of the population in the HGA nonattainment
area. Based on population, the county is over two times as large as Liberty,
Chambers, and Waller combined. Its NO
x
emissions
are significantly greater than the three counties being excluded from the
adopted rule. The estimated actual emissions from lawn and garden service
equipment in Montgomery County is 0.137 tpd of NO
x
and 5.607 tpd of VOC. The effect of delaying these emissions is expected to
result in equivalent emission reductions of 0.03 tpd of NO
x
and 1.68 tpd of VOC.
Sierra-Houston resubmitted comment letters dated August 2, 1999, January
31, 2000, and February 24, 2000, concerning already-completed rulemakings
and SIP revisions which Sierra-Houston had initially submitted during the
comment period for these previous rulemakings and SIP revisions.
These comments were addressed in the ANALYSIS OF TESTIMONY section of the
preambles to the earlier rulemakings and SIP revisions which were published
in previous issues of the
Texas Register
.
GEHC, MCA, and 13 individuals stated that facilities that predate the commission's
air permitting requirements (i.e., those that are "grandfathered") should
be subject to the NO
x
emission specifications.
GHASP commented that all grandfathered facilities should be investigated to
be certain that they are properly so designated since many of these facilities
have made modifications. State Senator Carlos Truan commented that a problem
with the proposed rules is that they do not deal with grandfathered facilities
and that the commission has let these facilities avoid permitting through
the use of standard exemptions.
The commission made no change in response to the comments. The adopted
rules that apply to facilities, for example the Chapter 117 NO
x
requirements and the Chapter 115 VOC requirements, apply to both
permitted and non-permitted ("grandfathered") sources in HGA. The commission
agrees that it is appropriate to pursue cost-effective measures to reduce
pollution; however, any such measures must be within the statutory authority
of the commission. The TCAA does not authorize the commission to require grandfathered
sources to obtain permits in order to operate, or to prohibit operation of
those sources. A grandfathered facility is one that existed at the time the
Texas Legislature amended the TCAA in 1971. These facilities were not required
to comply with (i.e., were grandfathered from) the then new requirement to
obtain permits for construction activities. Whenever a grandfathered facility
is modified (as that term is defined in the TCAA) then it is required to comply
with the TCAA permitting requirements in order to be authorized to construct
and operate that modification. If a grandfathered facility has never been
modified, it continues to be authorized by the TCAA to operate without a permit.
Further, the definition of "modification" specifically excludes changes to
facilities that are authorized by an exemption, i.e., any facility, including
a grandfathered facility, can make a change using a commission exemption (now
permit by rule) and this change is not considered to be a modification that
would trigger the permitting requirements of the TCAA. During the 76th Texas
Legislative Session in 1999, the issue of grandfathered sources was addressed
by two different legislative programs. Senate Bill 766 was passed which provided
a framework for a voluntary permitting program for grandfathered sources under
the TCAA, and SB 7 which requires mandatory permitting and emission reductions
from electric generating facilities. The commission continues to pursue enforcement
action against companies who are not in compliance with the permitting requirements
of the TCAA. However, SB 766 does provide for amnesty from enforcement for
facilities eligible to participate in the voluntary emission reduction permit
program as long as a permit application is received before the TCAA deadline
of September 1, 2001.
LWV-TX commented that the rule, while it may cause a public backlash, allows
enough time for the replacement of old equipment with newer, less polluting
equipment by homeowners and lawn services.
The commission revised the adopted rule to allow domestic and emergency
use of use lawn and garden service equipment powered by small, spark-ignition
engines 25 hp and below from April 1 to October 31 of each year. The adopted
rule specifically prohibits commercial operators and persons not exempt under §114.452(b)
from using the lawn and garden service equipment during the specified time
periods unless they submit an emissions reduction plan by May 31, 2003 that
will provide equivalent reductions of NO
x
and
VOC. The executive director may allow plans to be submitted after May 31,
2003. In any event, a plan must be approved prior to the use of that plan
for compliance with the requirements of this division. The commission agrees
that the April 1, 2005 compliance date should provide enough time for commercial
operators to make the necessary adjustments in order to comply with the rules.
Sierra-Houston and seven individuals commented that they believed that
this rule should include a complete ban on leaf blowers. Sierra-Houston added
that leaf blowers create noise and water pollution and that users of leaf
blowers blow organic debris into the storm sewer and that this will load up
streams with organic matter that will cause oxygen depletion and fish kills.
One individual commented that if this rule is applied to the HGA, then there
should be a rule to limit the use of drive-through windows. One individual
commented that a ban should be placed on all gasoline-powered golf carts in
favor of electric. Two individuals commented that they do not like loud lawn
equipment in the morning. TAB, Lynn's, Harris Landscape, and TNLA commented
that the rule would increase noise pollution because it compresses the work
day.
Because the proposed rule did not address drive-through windows, or gasoline
powered golf carts, the commission is unable to revise the rules at adoption
to include limitations to address these issues. Further, the proposed rule
did not address a ban on leaf blowers; therefore, the commission is unable
to adopt such a ban at this time. This adopted rule will prohibit the use
of leaf blowers and equipment like it, until afternoon during the specified
time periods. The commission realizes that idling vehicles are contributors
of emissions and is concurrently adopting a rule which will limit the amount
of time that very large, heavy-duty vehicles may idle. Leaf blowers are noisy;
however, the commission does not have the statutory authority to address issues
related to noise pollution. This rule will shift lawn maintenance activity
into the afternoon hours and should cause a decrease in lawn maintenance noise
in the morning hours. The commission disagrees that the compression of the
work day will increase noise pollution.
One individual commented that there should be "significant" emission reductions
from this rule if it is to be implemented, and three individuals wished to
know what benefits would be gained by this proposal. OPEI, PPEMA, Texas Lawn
and Landscape, and three individuals commented that limiting lawn mower emissions
would result in small reductions of NO
x
. PPEMA
and one individual commented that this rule is not necessary in terms of the
amount of pollutants that are being reduced. Ray's and six individuals commented
that they would like to know what the percentage of improvement would be attributable
to the proposed rule.
The commission believes the emission reduction that will result from these
rules is significant. The commission estimates that this measure will achieve
a minimum of 0.23 tpd delay of NO
x
until after
noon. There will also be a 12.4 tpd delay in VOC emissions until after noon.
Because the emission of NO
x
and VOC, both precursors
to the formation of ozone, will be delayed until after noon, this delay will
lead to a reduction in ozone that is equal to approximately 4.6 tpd NO
One individual commented that proper maintenance of lawn equipment must
be part of the solution.
The commission agrees with this comment and encourages operators of this
equipment to practice regular maintenance. Poor maintenance of internal combustion
engines can contribute to emissions of VOC and NO
x
.
One individual asked why the commission chose to implement the lawn mowing
rule in 2005, rather than earlier.
The commission chose to implement the lawn equipment time-shift rule in
2005 so that this rule may coincide with the new Division 9, Houston/Galveston
Construction Equipment Operating Restrictions; to Subchapter I, Non-road Engines;
Chapter 114, Control of Air Pollution from Motor Vehicles that is being adopted
concurrently with these rules. Additionally, by having the rules take effect
in 2005, this allows commercial operators and persons not exempt under §114.452(b)
to adjust to the impending change in schedule. That is, commercial operators
can determine whether they would like to alter their fleets to include manual
or electric-power lawn and garden service equipment or submit an emission
reduction plan under §114.452(c).
One individual commented that the rule is only being proposed because the
companies being regulated do not have influence over the commission.
Industry of all size, as well as individuals, are being asked to lower
emissions for the benefit of cleaner air in the HGA area. For instance, large
industries such as power companies, will be required to reduce their NO
Pate and Pate and CAP commented that the rule has not been attempted anywhere
in the United States. They also commented that the rule will result in an
average increase of 10% in their payroll and that the rule may cause many
workers to become unemployed. Missouri City commented that this rule will
create higher costs associated with the change in work schedule and the hiring
of part-time employees. TNLA, Harris Landscape, and Lynn's commented that
landscape workers often hold two jobs and this would not allow them to work
at their night jobs. ACEC, AOPE, BCCA, TNLA, CSE, EETC, RDC, TSDA, OPEI, PPEMA,
DACC/Dayton Pipe, NASA, Lynn's, Bio Energy, Frazier, Mustang Mowing, Spring
Valley, ExxonMobil, Harris Landscape, Wakefield, Ray's, Wiccacon, Johnson
Saw, Texas Lawn and Landscape, and 27 individuals commented that they felt
that the rule proposal would have too much of a negative impact on the lawn
mowing industry. TNLA and Harris Landscape added that this proposal could
create an unfair competitive advantage for those who choose to ignore it.
TAB commented that the rule would give a competitive advantage to doing business
outside of HGA. ExxonMobil commented that it does not support the use of temporal
restrictions on the use of non-road equipment such as lawn service equipment
and that the rules would be extremely disruptive to business and industry
in the region and will place the region at a competitive disadvantage relative
to other parts of the country. One individual requested to know the "economic
trade-offs" involved in the rule proposal, and the "major assumptions used"
for the proposal. Mustang Mowing and two individuals commented that sales
tax revenue will be lost. RDC, TNLA, Harris Landscape, Lynn's, Minnesota City,
Pate and Pate, Mustang Mowing, Wakefield, Ray's, and four individuals commented
that this rule will leave less time for companies to work, thus cutting into
their profits earned. RDC commented that they would be forced to cut wages
or increase prices to consumers. Greenscape commented that they begin mowing
at 7:30 a.m. and finish near 4:30 p.m. each weekday, with employees taking
several breaks during the hottest part of the day. This schedule meets the
budgets of their customers and provides employees with full time employment.
Harris County Judge Robert Eckels and City of Houston Mayor Brown commented
that the rule does not reduce pollution in a cost-effective or acceptable
manner for the residents, business, or government in the Houston region. Greenscape
commented that equipment has been purchased over the years with an eight-hour
day as the basis for the costs. Losing half a day will cut productivity and
sales. Hiring more employees would be more than their limited profit margin
could bear and that they could be forced out of business. Financial committments
made to creditors would likely not be met if the time restrictions were implemented.
The rule sacrifices the health of landscape businesses (with statewide sales
of nearly $4.4 billion per year) as well as their employees for the convenience
of others. TSDA, TNLA, Harris Landscape, Lynn's, Wakefield, and two individuals
commented that the basis and analysis for the rule is flawed.
Although it is true that this strategy has not before been implemented,
the commission believes that it is reasonable, based on known and credible
science, to regulate the use of lawn and garden service equipment powered
by small, spark-ignition engines 25 hp and below from April 1 to October 31
of each year in order to meet the federal ozone NAAQS.
The commission disagrees that this strategy is unproven, untested, or is
not based on sound science. It has been well established by the scientific
community that emissions of NO
x
released during
the late morning hours contribute more to ozone formation than do emissions
at other times of the day. This is because ozone is formed through chemical
reactions between natural and man-made emissions of VOC and NO
x
in the presence of sunlight. Higher ozone levels occur most frequently
on hot summer afternoons, and the critical time for the mixing of NO
Consequently, and understanding that a certain amount of lawn and garden
service equipment emissions are unavoidable, the commission believes that
delaying NO
x
emissions from the morning hours
until after noon, during the prime ozone forming months, is an effective and
well- reasoned strategy that uses good science to good effect.
The commission recognizes that compliance with this rule may cause losses
in productivity and revenue and require commercial operators to seek creative
solutions in order to remain competitive. The commission also recognizes that
members of the affected workforce may choose to seek other jobs with different
hours. However, the commission anticipates that affected companies will find
and make the necessary adjustments to minimize these impacts, especially considering
the far more substantial impacts that would result from the failure of the
HGA area to attain federal air quality standards that these rules are designed
to help achieve. Although many of the rules included in the current SIP attainment
strategy will not be easy to implement and will cause many of the affected
entities to adjust normal operations, these rules are necessary in order to
demonstrate compliance with the ozone standard.
As with any rule, the commission expects that there will be noncompliance
by an undetermined number of regulated entities. The commission believes that
most commercial operators will willingly comply with the regulation. Those
who do not will be subjected to the appropriate enforcement procedures. Economic
gain as a result of the violation is a factor in setting penalties.
The adopted rule includes an option for commercial operators to submit
an emission reduction plan that, if approved, will allow the operator to use
the prohibited equipment in the morning hours. The commission believes that
this flexibility will enable commercial operators to remain competitive. Further,
the adopted rule does not ban all work in the morning hours, rather, it prohibits
the use of certain equipment. Commercial operators will be able to use electric
or manual powered equipment before noon. This rule will result in the equivalent
of approximately 4.6 tons every day of NO
x
-equivalent
emissions reductions in the entire Houston/Galveston area. The commission
believes this to be a significant reduction of harmful emissions in an area
of the state classified as "severe nonattainment."
SBU Texas commented that it does not believe a serious attempt was made
to determine the actual economic impact of the rule on small businesses. More
needs to be done to justify the economic impact of the rules on small businesses.
The rules should concentrate on implementing cost-effective measures that
balance competing interests and proven methods that achieve results. Johnson
Saw commented that the rule would seriously affect small business owners in
the lawn and garden fields of operation. Bio Energy and Mustang Mowing commented
that the lost hours for working will require the doubling of equipment and
vehicles used which will cause prices to be higher, resulting in lost contracts,
with the potential of bankrupting smaller companies. Mustang Mowing, Bio Energy,
and two individuals added that larger companies would then pick up the business
from the small businesses and that this rule will create monopolies as smaller
lawn maintenance businesses find it impossible to compete. If there are not
enough small businesses, there will not be enough companies to fill the demand
for services. The monopolies could charge whatever they want for their services
and they will be able to pay their workers less because of the large availability
of unemployed workers. As a result of the loss of small businesses, sales
tax revenue will be lost. One individual commented that the rule will hurt
the small businessman. One individual commented that the rule would dictate
the time that small businesses could start their business. Pate and Pate commented
that the rule was rejected in California due to the burden it would have placed
on small business. Johnson Saw commented that the rule would seriously affect
small business owners in the lawn and garden fields of operation.
For several years, the commission's Small Business Assistance program has
provided help to small businesses in the areas of permitting, compliance,
and pollution prevention. Through this experience, the commission has gained
an understanding of the needs of small businesses and the impacts that additional
regulation can have on a small businesses. However, because of the need to
obtain significant reductions in the HGA nonattainment area, the commission
is unable to exempt small businesses from compliance with the rules. Even
though a business may be small, it may not have a small amount of emissions,
thus it is important that the emissions from small businesses be included
in these rules and in the SIP in order for the HGA area to reach attainment.
In order to provide as much flexibility as possible to all businesses that
must comply with the rules, the commission has revised the HGA SIP to allow
for the inclusion of economic incentive programs as a component of the HGA
SIP for future consideration.
The proposal preamble acknowledged that there may be fiscal implications
for small businesses as a result of the adoption and enforcement of the rules.
The proposal noted that the economic impacts were not anticipated to be significant
and that they would not likely extend beyond any impact due to the shift in
work schedules and possible implications from work delays. The commission
did state that additional employees might have to be hired or additional equipment
might be purchased. The commission received comments stating that equipment
for commercial lawn and garden operations is replaced regularly on a two-
to four-year cycle. Based on this information, the commission believes that
capital expenditures resulting from commercial operators' compliance with
the modified rule are within the normal replacement schedule of their equipment
and will not require the doubling of equipment or vehicles. For example, replacement
of existing inventories with electric equipment will allow operators to continue
their operations in the morning hours. The commission believes that replacement
of equipment could allow commercial operations to continue to operate with
the same number of employees after the 2005 implementation date. Further,
additional comments indicate that the primary expense for these businesses
is labor. The adopted rule allows commercial operators and persons to submit
emission reduction plans by May 31, 2003, for approval by the executive director
and the EPA no later than May 31, 2004. If an acceptable plan is submitted,
commercial operators will be exempt from operating hour restrictions upon
implementation of these rules in 2005 or thereafter, and will be able to operate
during the restricted hours. This would also eliminate or reduce the need
for increased labor costs. The executive director may allow plans to be submitted
after May 31, 2003. In any event, a plan must be approved prior to the use
of that plan for compliance with the requirements of this division. The commission
believes that these options will allow small businesses to continue to compete
with larger operations. These alternatives would enable small businesses to
take advantage of economic incentive programs which are developed in the future.
The commission will continue to work with small business representatives to
identify options for compliance which may currently exist or which may become
available in the near future.
Lynn's, TNLA, NASA, City of Simonton, Society of St. Vincent De Paul, Pate
and Pate, Harris County Judge Robert Eckels, City of Houston Mayor Brown,
BCCA, Harris Landscape, Pampered Lawns, Personal Expressions, and nine individuals
expressed concern for lawn maintenance worker's general welfare. NASA expressed
concerns for the safety and health of its onsite personnel since their workers
would be working in the hottest part of the day. The City of Simonton, Society
of St. Vincent De Paul, and RDC commented that the rule would have workers
trying to maintain the same number of properties in half the normal time during
the hottest part of the day and this would put the workers at a serious health
risk. TNLA commented that the rule would require employees to work in excessive
heat. TAB commented that workers would be subject to heat exhaustion. AAA
expressed concerns about stress on crews due to hot temperatures, not only
during the summer months but year round. Working after daylight hours will
increase the chance of accidents. Cornelius commented that workers will be
at a greater risk of heat stroke and that, according to OSHA (the Occupational
Safety and Health Administration), employers should schedule these types of
jobs for the cooler part of the day. This is a point widely taught in employee
training meetings on preventing heat stress. Excalibur and Pate and Pate commented
that the proposed workday shift poses an adverse health and safety threat
to workers and that shifting work to the evening hours is irresponsible and
unnecessary and poses a tremendous threat to the safety of workers and the
public. Lynn's commented that landscape employees will suffer in terms of
health if they have to start work at noon during daylight savings time. Mustang
Mowing commented that the rules will result in increased incidences of dehydration,
heat exhaustion, heat stroke, and skin problems related to mid-day sun exposure,
including but not limited to melanoma. Spring Valley commented that the 125
part per billion, one-hour ozone standard is a health based standard and that
no analysis was presented on the risks to human health and safety of operating
lawn service equipment in the heat as required by the rule. The City of Simonton
commented that the proposed rule is not reasonable and is dangerous to the
health of workers. ED commented that this strategy fails to recognize that
workers start work at dawn and quit at two or three to avoid hot temperatures.
BCCA commented that it is concerned that the shift of this vigorous outdoor
activity to the late afternoon and early evening hours present a safety hazard
to lawn service workers. Greenscape commented that restrictions on hours of
operation would be hard on employees and would cause an increase in costs
for consumers since the health risks would require higher prices to cover
the potential risks. RDC commented that lawn maintenance workers would experience
health risks. One individual commented that there would be an increased risk
of skin cancer for workers if they are obligated to perform their duties after
12:00 p.m. NASA, AAA, ED, RDC, BCCA, REI, OPEI, AOPE, TSDA, EETC, TNLA, TAB,
CSE, City of Galveston Public Works, ExxonMobil, Phillips 66, Bell, Cornelius,
Pate and Pate, Mustang Mowing, Spring Valley, Beasley, Lynn's, Wakefield,
Missouri City, Harris Landscape, Briggs & Stratton, Ray's, Wesly, Wiccacon,
Texas Lawn and Landscape, and 73 individuals commented that proposing an operating
delay on lawn equipment until after 12 p.m. during the hottest months of the
year would be unhealthy, especially for the elderly and/or infirm.
The commission agrees that this rule could negatively affect some in the
lawn care industry in terms of working conditions. The commission recognizes
that this rule may result in increased exposure to elevated temperatures,
increased fatigue, and perhaps increased health care costs for employers and
employees. However, operators of lawn equipment would be expected to take
all necessary measures to protect their health and safety and educate themselves
about potential risks as the commission presumes they do currently. The ultimate
responsibility of the commission in terms of this rule is to maintain and
improve the air quality and public health in the HGA. This rule would do that
by creating a reduction in NO
x
equal to approximately
4.6 tpd. These reductions are a necessary measure for successfully demonstrating
attainment. While high temperatures can be dangerous to many in the Houston/Galveston
area, every citizen in the area, especially asthmatics, the very young, and
the very old, are vulnerable to the effects of ground level ozone. The commission
is aware of the economic and other difficulties this rule will impose on businesses
and individuals, and is adopting it with an extended compliance schedule so
that lawn and maintenance businesses may supplement their equipment with electric
or manual powered units or develop an emissions control plan.
TNLA, Harris Landscape, Lynn's, Mustang Mowing, Excalibur, Pate and Pate,
TCSE-HC, and two individuals commented that the restriction would have a negative
economic impact on the minority community employed in the lawn service industry.
CAP, Lynn's, BCCA, OPEI, Spring Valley, Harris County Judge Robert Eckels,
City of Houston Mayor Brown, and 13 individuals expressed concern for the
low-income community employed in the lawn service industry. TNLA commented
landscape workers often hold two jobs so this would impact the ability of
these workers to continue in the second job and that the proposal would place
an undue burden on the Hispanic community because 85-90% of the landscape
workforce is Hispanic. Employees of landscape firms are semi-skilled laborers
for whom a day or week or no work may mean the difference between living above
or below the poverty line. Spring Valley and CAP commented that the proposed
rule does not contribute to attainment of the ozone standard at the lowest
economic and social cost because the proposal places a significant burden
on many of HGAs most vulnerable workers. Mustang Mowing commented that the
proposed ban could have widespread and negative effects on unskilled workers
and on minority workers. Two individuals commented that pay would be cut in
half for workers. Excalibur and Pate and Pate commented that the workday shift
would fall disproportionately on the minority community and that minority
families will feel a disproportionate impact. Seven individuals commented
that the restriction would have a negative economic impact on the minority
and/or low-income community employed in the lawn service industry. BCCA commented
that it is concerned that the impacts of the rule will fall disproportionately
on small and historically disadvantaged business owners. The commission maintains
that the rule as adopted will not have a disparate impact on persons based
on income level, race, color, or national origin. The basis for the rule is
protection of human health and the environment, and shifting emissions from
lawn and garden service equipment from 6:00 a.m. to 12:00 p.m. has been demonstrated
to provide benefits in reducing ozone formation. Although it is not clear
what, if any, legal standard the commentors allege the commission would violate
in adopting the rule, some state that the rule would "disproportionately impact"
minorities. This is clearly a reference to Title VI of the Civil Rights Act
of 1964. In order for the commission to be shown in violation of Title VI,
a disproportionately negative impact to minorities must be shown. As for potential
negative impacts of the rule, these are clearly borne equally by all commercial
operators and their employees governed by the rule without any differentiation
by race, color, or national origin. The ultimate responsibility of the commission
with these rules is to maintain and improve air quality and public health
in the HGA area. This rule would do that by creating a reduction in NO
The adopted rules provide that commercial operators can submit an emission
reduction plan, that if approved, will enable the operators to use the prohibited
equipment during the morning hours. The commission received comments stating
that equipment for commercial lawn and garden operations is replaced regularly
on a two- to four-year cycle. For example, this would allow operators to replace
a substantial portion of their current inventory with electric equipment prior
to the 2005 rule implementation date. Because the adopted rules do not prohibit
all lawn and garden service activities, just the use of certain equipment,
during the morning hours, commercial operators would be able to use the replaced
equipment in the morning. This would reduce any negative impacts on employees.
Lynn's, Spring Valley, Harris Landscape, Ray's, and four individuals commented
that this rule will cut into the "family time" of lawn and garden workers
because these workers will have to spend more hours away from home working
to make up for the time they will lose between 6:00 a.m. and 12 p.m. TNLA,
Excalibur, Pate and Pate, and AAA commented causing workers to work into the
evening hours will have an impact on the time that can be spent with their
families. Excalibur and Pate and Pate commented that workers might choose
to leave the industry or be forced into unemployment to avoid the extended
hours. CAP, Harris County Judge Robert Eckels, and Spring Valley commented
that the proposed rule does not contribute to attainment of the ozone standard
at the lowest social cost because the proposal places a significant burden
on many of HGA's most vulnerable workers. TAB commented that thousands of
individuals who are accustomed to being at home with their families in the
evenings would no longer have that option causing a tremendous negative impact
on those families.
The commission recognizes that these rules may initially cause certain
disruptions to the personal and social lives of affected employees, however
the rules have been revised to provide flexibility for commercial operators.
The adopted rules do not prohibit all lawn and garden services from being
done in the morning hours, rather it prohibits the use of lawn and garden
service equipment that is powered by small spark ignition engines of 25 hp
or less. Work can still be done in the morning for activities that do not
require the use of the prohibited equipment or electric or manual powered
equipment may be used. Further, commercial operators may submit an emission
reduction plan that, if approved, would allow the commercial operator and
its employees to continue to work in the morning hours using the prohibited
equipment. The restriction on hours of operation of certain lawn and garden
service equipment is an important component in the overall strategy to reduce
peak ozone levels to enable the HGA area to attain federal ozone standards.
The area's failure to attain these standards will significantly impact the
area economy, and therefore the quality of life of its citizens and communities.
GEHC, Cornelius, Wakefield, and 15 individuals commented that limiting
lawn mower emissions would result in only small reductions of NO
x
, and that the real source of most emissions was large industry. One
individual commented that their mowing does not have the same effect as the
pollution created by refineries in the Pasadena area. PPEMA commented that
lawn and garden equipment engine are minor contributors to the VOC and NO
The commission agrees that the largest stationary sources of NO
x
are point sources such as power plants and refineries. However, non-road
mobile sources are also significant contributors of NO
x
emissions and are a factor to be considered in reaching attainment.
Lawn and garden equipment accounts for approximately 41 tpd of VOC. Small
engines are the largest VOC emitters in the non-road category. Lawn and garden
equipment accounts for 37% of the 2007 HGA eight-county area non-road VOC
total and recreational boating accounts for an additional 23% on weekdays,
and on weekends their share is much higher. This total includes emissions
from four-stroke and the higher emitting two-stroke engines. The other 40%
is spread among many categories. The 41.2 tpd of VOCs from lawn and garden
equipment account for approximately 6.5% of the total anthropogenic eight-county
VOCs. This rule will result in a reduction in ozone that is equal to approximately
4.6 tons per day of NO
x
emissions and 12.4 tpd
in VOC emissions for the HGA nonattainment area during the specified time
period. The CARB has stated that "using a commercial chain saw powered by
a two-stroke engine for two hours produces the same amount of smog-forming
hydrocarbon emissions as driving ten 1996 cars about 250 miles each." Model
year 1996 cars are equipped with advanced fuel injection systems and sophisticated
three-way catalysts that enable the cars to burn nearly all of their fuel,
and the catalyst to oxidize a large fraction of what is not consumed. A two-stroke
chainsaw, with a simple carburetor, low- compression ratio, and no catalyst,
can emit a proportionally vast amount of VOC as an unburned mix. According
to EPA estimates, in many large urban areas, pre-1997 lawn and garden equipment
accounts for as much as 5% of the total man-made hydrocarbons that contribute
to ozone formation. The commission expects that reducing emissions from small
engines will help to reduce the formation of ground-level ozone, thus resulting
in a decrease of air pollution-related health problems for urban residents.
The commission believes this to be a significant reduction of emissions in
an area of the state classified as "severe" in terms of ozone nonattainment.
By shifting the hours of use for handheld and non-handheld spark-ignition
lawn and garden service equipment until after noon, NO
x
emissions from such equipment will not mix in the atmosphere with
other ozone-causing compounds until later in the day. The commission agrees
that one individual's gardening routine does not emit the same types and/or
amounts of pollutants as an oil refinery. However, when combined, the thousands
of small spark-ignition engines used throughout the five specific counties
in the HGA subject to the adopted rule do emit high levels of NO
x
and VOCs. Additionally, it cannot be said that point sources will
not be affected by the rules being adopted by the commission at this time.
The commission is adopting rules which will require point sources in the HGA
to lower emissions by 90%. The ultimate responsibility of the commission in
terms of this rule is to maintain and improve the air quality and public health
in the HGA. These reductions are a necessary measure for successfully demonstrating
attainment in HGA.
RAQCG, AAA, SBU Texas, Mustang Mowing, BCCA, REI, Phillips 66, ExxonMobil,
MCA, Public Citizen, Harris County Judge Robert Eckels, City of Houston Mayor
Brown, GHASP, and 19 individuals believe the commission and/or EPA should
require makers of lawn equipment to produce cleaner-burning engines. One individual
commented that the commission should mandate the use of electric mowers in
the HGA starting on October 1, 2003. BCCA commented that the commission and
the EPA should work to develop and implement the next generation of lower-emitting
lawn service equipment, and press for its early introduction into the Texas
market. Three individuals suggested that distributors of lawn equipment should
not be allowed to sell heavy polluting lawn equipment. One individual commented
that this rule will stimulate lawn care companies to utilize clean-burning
equipment. Sierra-Houston commented that the commission should require that
some or all lawn and garden equipment be electric-powered.
The commission did not propose the control measures mentioned by the commenters
and therefore cannot adopt them in this rulemaking. However, the EPA has adopted
rules that require stringent emission standards for non-road small spark ignition
handheld engines, such as trimmers, brush cutters, and chain saws. The second
phase of the EPA rulemaking will reduce VOC and NO
x
by an additional 70% beyond the current Phase 1 standards. The new
standards will be phased in beginning with the 2002 model year. These new
EPA rules will require manufacturers to develop engines that will emit significantly
less emissions.
AOPE, TSDA, and three individuals commented that small, spark-ignition
engines under 25 hp are being improved yearly and therefore believe that the
rules are not necessary.
The commission agrees that small, spark-ignition engines under 25 hp are
being improved but disagrees that this improvement justifies not adopting
the rules. The commission continues to believe that the adopted rule is a
necessary component of the HGA SIP demonstration. The commission cannot eliminate
the adopted rule without an established, quantifiable, and enforceable replacement
strategy that demonstrates proven ozone reductions equivalent to those achieved
by these rules. The commission cannot do away with the operating restrictions
because of the significant contribution of emissions from lawn and garden
service equipment to the HGA area high ozone levels. NO
x
is a key component in the formation of ozone. Because of this significant
contribution that the equipment affected by these rules make to the HGA area
ozone levels, it is essential that the small spark-ignition engine operating
restrictions rules be implemented along with the other rules and measures
included in this SIP revision in order for the HGA area to demonstrate attainment
with the federal ozone standard. The restriction on hours of operation of
non-road, spark- ignition engines 25 hp and under is an essential component
to the overall strategy to reduce peak ozone levels to enable the HGA area
to attain federal ozone standards.
AOPE commented that this rule would affect anyone who utilized a small
engine such as plumbers and carpet cleaning companies.
The commission agrees that if plumbers and carpet cleaning companies use
handheld equipment such as trimmers, edgers, chain saws, leaf blowers/vacuums,
and shredders or non-handheld lawn and garden equipment such as walk-behind
lawnmowers, lawn tractors, tillers, and small generators, they would be affected
by the adopted rule.
Mustang Mowing and four individuals commented that electric lawn equipment
is not a viable option. Three individuals commented that they felt that electric
lawn equipment was an excellent alternative to gas-powered equipment. One
individual stated that electric-powered lawn equipment costs too much in comparison
to gasoline-powered equipment. One individual commented that their lawn servicing
company which used push mowers, rechargeable weed eaters, and blowers purchased
at Sears were less expensive than gas-powered equipment. The individual also
commented that this equipment needed less maintenance and was less dangerous.
Workers reportedly enjoyed the lighter weight of the equipment, and the customers
were pleased with its performance.
The commission disagrees that electronic lawn and garden service equipment
is not a viable alternative to small spark-ignition engines. This equipment
can be purchased at most stores where gas- powered mowers can be found. This
equipment is quiet, lightweight, and can perform the same duties as gas-powered
equipment without any emissions of NO
x
or VOC.
The commission agrees that the initial purchase of electric-powered equipment
is more expensive than gasoline-powered equipment. However, the commission
believes that this increase will be offset through the life of the equipment
due to reduced fuel and maintenance costs. It is not a requirement of this
rule that one purchase electric lawn equipment only. There are electric and
manual powered versions of edgers/trimmers, lawn mowers, and chain saws.
Mustang Mowing, TLS, Ray's, City of Galveston Public Works, and five individuals
commented that they did not understand how shifting the time period during
which lawn equipment may be used will benefit air quality. CBE, MCA, TNLA,
Harris Landscape, TAB, ED, OPEI, Lynn's, Sierra- Houston, Briggs & Stratton,
and five individuals commented that the rules do not eliminate emissions,
only shifts them to another time. ED commented that the proposal does not
reduce total NO
x
emissions. On ozone episodes
when an air mass leaving HGA re-circulates back into the region, the benefits
of the time shift in the release of the emissions may have little or no benefit.
The commission should reevaluate this strategy under re-circulation conditions.
Plus, the strategy will have little or no value in reducing ozone levels downwind
of HGA. Sierra-Houston also commented on re-circulation and noted that this
proposal could make ozone formation potential worse because emissions will
not actually be reduced but will simply feed ozone precursor clouds with additional
pollutants over time. MCA commented that there must be real emission reductions
and that postponing emissions to later in the day is not a real reduction.
Spring Valley, Mayor Louise Richman - City of Spring Valley, and one individual
commented that these rules should only be applied during those months when
it is absolutely necessary (i.e., limit the ban to days with high ozone generation
potential). One individual commented that this rule should require that lawns
only be mowed every other week. One individual asked why this ban would take
place during daylight-saving time. One individual commented that the commission
should allow mowing from September through May 11, 6:00 a.m. to 12 p.m.
It has been well established by the scientific community that emissions
of NO
x
released during the late morning hours
contribute more to ozone formation than do emissions at other times of the
day. This is because ozone is formed through chemical reactions between natural
and man-made emissions of VOC and NO
x
in the
presence of sunlight. Higher ozone levels occur most frequently on hot summer
afternoons, and the critical time for the mixing of NO
x
and VOCs is early in the day. By delaying the hours of operation
for certain lawn and garden service equipment and delaying the release of
NO
x
emissions until after noon during the ozone
season, the NO
x
emissions will not mix in the
atmosphere with other ozone-forming compounds until after the critical mixing
time has passed. Therefore, production of ozone will be stalled until later
in the day when optimum ozone formation conditions no longer exist, ultimately
reducing the peak level of ozone produced. The commission believes that delaying
NO
x
emissions from the morning hours until after
noon, during the prime ozone forming months, is an effective and well-reasoned
strategy that uses good science to good effect. To achieve the greatest benefit
the rules must be in effect during the entire ozone season, because conditions
can be present at any time during that season for the formation of high levels
of ozone. The commission acknowledges that re-circulation occurs and can be
a factor in escalating daily ozone levels in Houston. As re-circulation occurs,
emissions are brought back into the HGA area on a daily cycle depending on
meteorological events such as a land/sea breeze. As this cycle occurs daily,
the time of day of the emissions makes little difference on whether the contaminants
will be returned on the subsequent day. The intent of this adoption is to
reduce the amount of time that sunlight has to react with ozone precursor
gases on. Therefore, the commission believes that re-circulation is not a
significant factor in the effectiveness of this adopted rule.
If the commission were to only permit the use of lawn equipment every other
week throughout the entire day, or only on ozone action days, the emission
reduction benefit of the rule would be diminished. The commission lacks sufficient
historical data on ozone action day prediction, as well as the technology
to improve upon prediction accuracies, to warrant changing the rules to only
be enacted on ozone action days. That is, the time shift does not allow the
use lawn equipment in the morning hours because this is the primary time during
which ozone-forming emissions mix with sunlight to create ground-level ozone.
It would also be difficult for commercial operators to comply with the rule
if the time periods for compliance were different from week to week. It is
important that the restriction on the use of lawn and garden service equipment
be in effect everyday from April 1 until October 31 since this is when HGA
experiences the greatest impact from ozone formation.
EPA commented that it understands that 100% rule effectiveness has been
assumed for the proposed rule. Since this will take a substantial commitment
of resources to approach that level of effectiveness, the commission should
document the resources that will be allocated for this measure to achieve
the full 100% projected benefit. Otherwise, a more realistic level of rule
effectiveness should be assumed. The PIC commented that it questioned the
likelihood of achieving 100% compliance with the proposed rule. The PIC seeks
a clarification regarding whether the commission prediction that the lawn
equipment operating restrictions will reduce NO
x
emissions in the affected area by 0.58 tpd is based on a presumption of 100%
compliance. If the commission prediction is based on 100% compliance, the
PIC suggests that the estimated annual NO
x
reduction
be recalculated to reflect the potential for noncompliance with the rule.
TNLA commented that the proposal is unlikely to have a positive impact since
it relies solely on modifying the behavior of potentially over a million operators
of outdoor power equipment and does not result in any actual emission reductions.
TNLA noted that EPA discounts SIP emission credits based on rule effectiveness,
compliance uncertainty and programmatic uncertainty so it is reasonable to
assume that a rule based solely on behavior modification will not be given
full SIP credit. TNLA again suggested adopting the California spill-proof
gasoline container rule as a cost effective means of obtaining over 70 tpd
of reduction of reactive organic emissions, which, in California, is expected
by 2010.
The adopted rule does not prohibit the use of lawn and garden service equipment
at a domestic residence by the owner of, or a resident at, the residence,
nor does it prohibit use by a non-commercial operator. The adopted rule applies
to commercial operators and persons who do not meet an exemption under §114.452(b).
The adopted rule includes an option for commercial operators to submit an
emission reduction plan that, if approved, will allow the operator to use
the prohibited equipment in the morning hours. The commission believes that
this flexibility will enable commercial operators to remain competitive and
will encourage compliance with the rules. Further, the adopted rule does not
ban all work in the morning hours, rather, it prohibits the use of certain
equipment. Commercial operators will be able to use electric or manual powered
equipment before noon. The commission believes that commercial operators will
make the necessary adjustments required to comply with the adopted rules.
The commission has re-evaluated the rule effectiveness for these rules and
continue to believe that the rule effectiveness will be 100%, especially since
the rules now apply only to commercial operators. The commission will enforce
the rules using its existing enforcement program, including working with local
programs to ensure the highest possible compliance rate.
TSDA, Wesley, and EETC commented that due to the fact that this rule does
not allow the use of any type of lawn equipment before 12:00 p.m., except
for manual and electric equipment, they cannot utilize natural gas-burning
mowers which have very low emissions.
The commission agrees that natural gas-burning mowers have low emissions.
However, any emissions from lawn and garden service equipment that is powered
by small spark ignition engines of 25 hp or less, will contribute to the formation
of ozone. Commercial operators may chose to lower emissions by other means
based on the new provision in §114.452, which allows commercial operators
to use the restricted equipment if they submit an approvable emission reduction
plan that will reduce an equivalent amount of emissions. An acceptable plan
might be one that is based on using natural gas-burning mowers during the
restricted time period.
RAQCG, ED, CAP, TNLA, TLS, OPEI, PPEMA, TAB, TSDA, EETC, Sierra-Galveston,
Sierra-Houston, Lynn's, Excalibur, La Porte, Pate and Pate, Spring Valley,
Harris County Judge Robert Eckels, Harris Landscape, City of Houston Mayor
Brown, Missouri City, State Representative Robert Talton, Wesley, and 27 individuals
commented that the proposed rule would be very difficult, if not impossible
to enforce, thereby being ineffective. Sierra-Houston commented that the rule
is virtually unenforceable since the commission and local air pollution agencies
do not have the investigators to ensure that the rules are enforced. County
Commissioner Malcolm Purvis, asked who would be responsible for enforcing
the rule, how the rule will be enforced, the cost of enforcement, and how
many people this will require. Spring Valley commented that municipalities
are concerned about requirements that their overworked and understaffed local
police departments will be required to enforce the rule and asked if municipalities
are not required to enforce the rule, what agencies will be responsible for
enforcement? Lynn's commented that the rule cannot be enforced and therefore
will not do any real good in reducing air pollution. TNLA commented that there
is no reasonable way to enforce the rule and noted that when laws are considered
to be excessively onerous by the public, they are usually ignored. PPEMA commented
the rule would be difficult to enforce. TAB, Pate and Pate, and Excalibur
commented that the rule is unenforceable and that enforcement would most likely
fall to local governments which are lacking in funding and manpower. This
will result in nonuniform enforcement, if there is enforcement at all. ED
commented about the ability to enforce the rule since there are scores of
independent lawn and garden companies in HGA. To enforce a rule concerning
starting times for this work will require a lot of police issuing tickets
and resources may be better spent preventing crime. One individual commented
that this rule would create a new class of lawbreakers. Three individuals
commented that new revenue would have to be raised to fund the enforcement
of this new regulation. Mustang Mowing commented that extra money will have
to be spent to enforce the ban, including extra police officers. This spending
could be applied to other more useful measures of reducing pollution like
better mass transit programs. Sierra-Galveston commented that the SIP calculates
unrealistic NO
x
reductions from a ludicrous restrictions
like the lawn ban. People are going to mow their lawns whenever they please.
Mustang Mowing and three individuals commented that having to raise new revenue
to fund the enforcement of this new regulation would be problematic.
The commission agrees that the rule, as proposed, presented enforcement
challenges for the commission, cities, and local programs. However, the commission
believes that the adopted rule will be less of an enforcement challenge since
it now applies only to commercial operators. The commission believes that
these entities will take appropriate measures to comply with the adopted rules.
As with all of its rules, the commission will enforce the requirements after
the rule compliance date and take appropriate action for noncompliance situations.
The rules are enforced by staff in the commission's regional offices, as well
as local air pollution control programs. Local governments have the same power
and are subject to the same restrictions as the commission under TCAA, §382.015,
Power to Enter Property, to inspect the air and to enter public or private
property in its territorial jurisdiction to determine if the level of air
contaminants in an area in its territorial jurisdiction meet levels set by
the commission. Local governments are not required to enforce commission rules
but may sign cooperative agreements with the commission to enforce the rules
under TCAA, §382.115, Cooperative Agreements. Local programs can also
enforce commission rules without signing a cooperative agreement. The authority
of local governments to enforce air pollution requirements is specified in
detail in TCAA, §§382.111 - 382.115, and local governments can institute
civil actions in the same manner as the commission pursuant to Texas Water
Code (TWC), §7.351. The commission will work with local officials to
ensure enforcement of the SIP and SIP rules. The commission has existing relationships
with pollution control authorities in the City of Houston, Harris County,
and Galveston County for enforcement of other commission rules. The agency
will continue enforcement relationships with these entities and develop relationships
with other local officials as needed to create effective enforcement mechanisms
for the SIP and SIP rules. The commission expects to enforce this rule with
existing personnel and does not anticipate any increase in enforcement costs.
Five individuals commented that this rule could interfere with their ability
to comply with local lawn control rules which require their lawns to be maintained
to certain standards.
The commission is not banning lawn maintenance activities altogether, merely
shifting the time period during which lawn work may be conducted with small
spark-ignition engines under 25 hp. There are alternatives to using this type
of gasoline-powered equipment, including the use of electric or manual equipment.
One individual requested that the commission encourage stores to stock
electric- and manual- powered lawn equipment. One individual commented that
they cannot find a store from which to purchase manual mowers.
Electric and manual mowers are available at many of the major hardware
stores. The commission supports the manufacture and sale of low- and zero-emission
technology currently. The commission anticipates that stock of electric and
manual powered equipment will grow as demand increases.
RAQCG, BCCA, REI, HARC CGS, Friendly Robotics, Bell, ExxonMobil, Houston
MPO, Phillips 66, Spring Valley, Harris County Judge Robert Eckels, City of
Houston Mayor Brown, Cornelius, and 14 individuals requested that the commission
provide monetary incentives for the purchase of clean-burning lawn equipment.
CAP, Harris County Judge Robert Eckels, and Spring Valley commented that the
proposal should be deleted from the SIP and replaced with a publically acceptable
alternative that is achievable and enforceable. This proposal should be included
in the economic incentive programs that are being developed for HGA. Public
Citizen commented that they would support the Carl Moyer program as is employed
in California whereby an enforceable, market- based incentive program is utilized.
The commission agrees that economic incentive programs can potentially
be an effective tool for achieving air quality. One such program is the Carl
Moyer program in California. That program appears to be successful in providing
flexibility to the regulated industry while still achieving reductions in
air emissions. The California program is authorized by and funded through
the state legislative process and such legislative approval does not currently
exist for a similar Texas program. The commission will continue to try to
identify economic incentives which it has authority to implement. Because
the commission agrees that market-based incentive programs can be an important
component in encouraging development of new technologies and / or greater
or more cost effective emission reduction strategies, the commission has provided
for the inclusion of economic incentive programs as a component of the HGA
SIP in the future.
The commission acknowledges the recommendation for a Carl Moyer-type program
to accelerate the development and introduction of emissions-reducing technology
for small, spark-ignition equipment 25 hp and under, but must rely on the
Texas Legislature for approval and grant funding to further such a project.
The commission staff will continue to study issues, interim solutions, and
the feasibility of implementing a similar state-wide pilot program.
In addition, local stakeholders in the HGA area have expressed an interest
in the creation of programs designed to provide incentives for the achievement
of earlier and/or greater reductions than anticipated from currently adopted
control measures. Such incentive programs could be effective technology-forcing
tools to obtain substantial innovation and ozone reductions in the most cost-effective
manner possible. Possible components of one such program applicable to these
rules could be the competitive provision of funds to entities operating both
on- and non-road NO
x
sources to assist in the
incremental costs of cleaner equipment, which could encourage earlier implementation
of new technologies, cleaner engines, and fuels. Other incentive programs
could focus on tax incentives, subsidies, research and development, technological
assistance, etc. The commission anticipates that such programs could be components
of the HGA ozone nonattainment SIP, either as enforceable commitments, as
potential future substitute measures based on per-ton reduction cost and total
funding associated with the final scope of the programs, or as alternative
methods of compliance with proposed control strategies.
SBU Texas commented it would support modifications of the proposal that
would give businesses a choice, for example, limited use of equipment as proposed
or the use of more efficient, less polluting equipment. Choices could bring
about even less pollution by providing an incentive to buy newer, more efficient
equipment. The proposed rules leave in place much of the older equipment to
operate during permitted hours. Spring Valley commented that there is no flexibility
in the proposed rule to allow development of alternative emission reduction
plans to this mandate. TNLA, TSDA, EETC, Harris Landscape, Lynn's, Spring
Valley, Houston MPO, and one individual commented that the lawn industry has
not been offered the same opportunity to present alternative plans that every
other regulated industry was offered. Metro recommended that an exemption
be provided for those entities that produce an approved emissions reduction
plan. TSDA commented that the rule should provide alternatives, including
consideration of using propane or alternative fuels. Public Citizen, La Porte,
Pate and Pate, and one individual expressed support for a plan whereby those
that use alternative fuels (e.g., LPG, CNG), and/or cleaner-burning equipment
be exempted from the rule.
The adopted rule has been revised to provide an option in §114.452(b)
for commercial operators to submit an emissions reduction plan by May 31,
2003, which must be approved by the executive director and the EPA no later
than May 31, 2004. If the plan is approved, a commercial operator would be
exempt from the operating hour restrictions upon implementation of these rules
in 2005, and would be permitted to operate during the restricted hours. The
commission is requiring submission of the emissions reduction plans two years
prior to the compliance date to allow adequate time for review of the plans,
both by the commission and the EPA, and to allow the commission to ensure
that the collective emission reductions achieved by the plans are equivalent
to the ozone reductions achieved by implementation of the rules. In order
to be approved, the plan must demonstrate NO
x
and VOC reductions equivalent to those required by the rules being requested
for exemption, and must contain adequate enforcement provisions. The executive
director may allow plans to be submitted after May 31, 2003. In any event,
a plan must be approved prior to the use of that plan for compliance with
the requirements of this division. This alternative to submit an emission
reduction plan would also enable commercial operators and persons to take
advantage of an economic incentive program which is to be developed in the
future. The commission will continue to work with industry representatives
to identify options for compliance which may currently exist or which may
become available in the near future. The commission does not believe it is
appropriate to exempt users of alternative fuels or cleaner burning equipment
from the adopted rules and instead have included the option to submit an emission
reduction plan. An emission reduction plan could be submitted that includes
the use of cleaner burning equipment, and alternative fuels, including propane.
Houston MPO commented that the rule should have the ability to create alternatives
in order to offset the mandates. The mechanism to provide the creation of
the offsets should be through the Voluntary Mobile Emission Program and/or
Economic Incentive Program. TNLA, Harris Landscape, Lynn's, and 2 individuals
suggested that the commission replace this rule with a voluntary program to
lower emissions from this equipment. The EPA commented that because of the
level of resources necessary, even if a more realistic rule effectiveness
level is assumed, this program might be more appropriately implemented as
a voluntary measure. RAQCG commented that the lawn equipment measures should
be included in a voluntary emission incentive program. BCCA commented that
the commission should develop a program which provides for voluntary emission
reduction incentives instead of adopting the rule. For example, lawn service
operators and citizens could receive a rebate for the incremental cost of
electric or low-emissions lawn service equipment in exchange for scrapping
old equipment, thus accelerating the turnover of newer technology in the region.
The EPA provides for the inclusion of voluntary programs or measures as
part of the attainment demonstration, but limits the amount of emission reduction
credit that may be claimed from such measures, due to the fact that the programs
are not enforceable mechanisms. In accordance with EPA policy, the commission
has included some voluntary programs as part of the HGA SIP. The Houston Galveston
Area Council (HGAC) is the entity responsible for the development and implementation
of these programs, which are detailed in the HGA SIP. The Voluntary Mobile
Source Emission Reduction Program (VMEP) is part of the Houston-Galveston
nonattainment area's attainment demonstration that the HGAC will be implementing.
HGAC will be responsible for the development and implementation of all VMEP
initiatives in the Houston-Galveston area. If this rule became voluntary it
could not be counted as an enforceable measure obtaining emission reductions
for the demonstration of attainment. As stated elsewhere in this preamble,
the emission reductions associated with this rule are necessary for the attainment
of the NAAQS in the HGA area. It is possible for voluntary measures to be
made enforceable through agreements and in that case they can be counted toward
the SIP. The commission encourages efforts to reach enforceable agreements
as suggested by the representative for the Mayor of Houston, and looks forward
to working with all interested participants. The commission does not believe
it can eliminate the operating restrictions in the adopted rule because of
the significant contribution that lawn and garden equipment makes to the HGA
area ozone levels. Because of this significant contribution that the equipment
affected by these rules make to the HGA area ozone levels, it is essential
that the equipment operating restrictions rules be implemented along with
the other rules and measures included in this SIP revision in order for the
HGA area to demonstrate attainment with the federal ozone standard.
RDC, PPEMA, City of Simonton, Poulan, and ten individuals commented that
the rule will harm homeowners. For instance, people will be left without service,
or be forced to pay more for services. One individual commented that this
rule will pose an unnecessary health risk to their family because they will
have to breathe the fumes of the gardeners' machines in the evening.
The adopted rule does not require a total ban on the use of small spark-ignition
lawn and garden service equipment, rather, it prohibits the use of this equipment
from 6:00 a.m. until noon from April 1 until October 31. Further, commercial
operators are able to use electric or manual powered lawn and garden service
equipment and may submit an emissions reduction plan which would allow them
to operate in the morning hours. Therefore, the commission does not believe
that homeowners will be left without service. The commission agrees that increased
costs for lawn service may be a result of this rule. However, it is more likely
that lawn mowing companies will be able to accommodate the needs of all of
their clients in a cost-effective manner by the time this rule is implemented
in 2005. The commission believes that the ability to use electric equipment
or an alternative plan will keep the need to perform lawn and garden work
in the evening hours to a minimum.
HARC, CGS, and two individuals suggestioned that those in the HGA area
use landscaping which requires less maintenance.
The commission supports the use of such techniques, also known as xeriscaping.
The use of xeriscaping - utilizing plant life which is adapted to the weather
conditions common to the region - saves money, water, time, and effort. Most
relevant to this discussion however is the fact that lawns planted with particular
grasses adapted to the weather of Texas can go for much longer periods of
time without the need to be mowed, hence reducing the need for the use of
gasoline-powered engines which contribute to ground-level ozone pollution.
Wakefield and three individuals commented that this rule should be applied
to the entire state.
The commission appreciates the commenters' support for state-wide applicability
of the rules. The commission notes, however, that it is not obligated to adopt
all rules statewide in order to satisfy its commitments under the SIP, nor
is the commission required to do so under the FCAA. Three of the adopted measures
contain emission reduction strategies that have been proposed for statewide
applicability: California large-spark ignition engines; emissions banking
and trading program (that portion of the adopted rule which relates to the
trading of emission reduction credits and discrete emission reduction credits);
and low-emission diesel fuel (that portion of the proposed rule which relates
to on-highway fuel).
In evaluating whether to implement all of the rules statewide, the commission
took into account many concerns, including, but not limited to, the need for
the marketplace to be able to respond to regulation, the possible impacts
on transport and distribution systems, the possibility of increased costs
and financial burdens on regulated entities, and regional needs and issues
associated with state-wide mandates. The commission analyzed where emission
reduction measures are most needed and where emission reduction measures will
be most effective in order to demonstrate attainment.
One individual commented that these rules are being set up to embarrass
Texas and the Governor, and that the State Legislators and Congress should
investigate these plans.
The commission disagrees with this statement. The commission intent is
to comply with the timelines provided in 1990 FCAA amendments and subsequent
EPA guidance for submitting rules to demonstrate ozone attainment in HGA.
Accordingly, Texas has committed to adopting the majority of the necessary
rules for the HGA attainment demonstration by December 31, 2000.
One individual requested that an exemption be made for those people who
could not mow after noon for health reasons.
The adopted rule exempts any use at a domestic residence by the owner of,
or a resident at, that domestic residence and any use by a non-commercial
operator.
One individual suggests that the commission study the strategies that California
has utilized to control ground-level ozone.
The commission is aware of the ozone control programs utilized by the State
of California and has one rule based directly on a CARB rule which sets emission
standards for spark-ignition engines above 25 hp. That rule is being adopted
concurrently with this rulemaking.
Greenscape suggested that a law should be passed to stagger the work times
of commuters so that auto emissions would be reduced.
The commission does not have the statutory authority to adopt a regulation
that would require the staggering of work times of commuters. However, HGAC
is reviewing an option to use a voluntary program for a reduction in vehicle
miles traveled (VMT) that could include such things as ride sharing, adjusting
work hours, and other commuter options. Any reductions resulting from that
program would be fully creditable to the SIP.
Dayton Pipe commented that it has over 13 acres of land to mow and maintain
and that it would be hard to do that in four-hour days unless they opened
at noon and worked until 8:00 p.m. One individual asked that those with many
acres of land should be allowed to mow during the ban period.
The adopted rule prohibits commercial operators from using lawn and garden
service equipment powered by small spark-ignition engines less than 25 hp
from 6:00 a.m. until noon from April 1 to October 31. This prohibition does
not depend on the amount of acreage being mowed. The adopted rule does not
prohibit all mowing, only that which is done with the specified engine type.
AAA, Excalibur, TNLA, Lynn's, Harris Landscape, and six individuals commented
that working during the night time to make up for lost morning hours is not
feasible and insurance costs for businesses may increase.
The commission understands that there may be economic impacts such as increased
insurance costs as a result of implementation of the adopted rule. However,
the cost to all citizens of HGA, including the regulated community, will be
significant if the area fails to comply with the FCAA ozone standards. The
effective period of this rule runs concurrently with daylight savings time.
This should help reduce potential risks associated with low visibility as
much lawn and garden maintenance activity will still occur in daylight. The
adopted rule does not prohibit all lawn and garden service work in the morning
hours. Commercial operators will be able to use electric or manual powered
equipment before noon. They can also submit an emission reduction plan, that
if approved, will allow the commercial operator to use the prohibited equipment
in the morning.
TNLA, Harris Landscape, and Lynn's commented that application of pesticide
and fertilizers should not occur during the heat of the daytime.
This rule does not prohibit the application of pesticides or fertilizers
during any part of the day unless they are applied with small spark-ignition
lawn and garden service equipment powered by an engine of 25 hp or less.
Personal Expressions commented that the fuel used in the type of equipment
covered under this rule is the source of harmful emissions. AOPE commented
that the commission should utilize a plan which would mandate the use of cleaner-burning
two-cycle engine oil.
The primary fuel for this type of equipment is either gasoline for four-stroke
engines or gasoline mixed with lubricating oil for two-stroke engines. The
gasoline used in four-stroke engines is not inherently dirty, and emission
levels from those engines are more dependent on engine maintenance rather
than the use of gasoline. The two-stroke is a higher emitting engine due to
its speed of operation and the greater viscosity of the fuel. The two-stroke
engine is useful because of its lighter weight and ability to operate in a
variety of positions. The commission believes that electric equipment is a
viable alternative to any gasoline equipment. The commission is not aware
of any cleaner burning two-cycle engine oil that has been certified for use
as a low emitting two-cycle additive.
TxDOT and one individual commented that an "emergency clause" should be
included in the rule which would allow them to operate chain saws, generators,
and gasoline-powered pumps in emergency situations (e.g., clearing fallen
trees from the roadway, etc.).
The commission agrees with the commenters. An exception was added in §114.452(b)
which allows the use of small, spark-ignition engines 25 hp and below to be
used exclusively for emergency operations to protect human health and safety
or the environment, including equipment being used to repair facilities, devices,
systems, or infrastructure that have failed, or are in danger of failing,
in order to prevent immediate harm to public health, safety, or the environment.
PPEMA, TNLA, and Cornelius commented that the commission should encourage
state and national lawn and landscape associations to serve as training and
educational resources in communicating with commercial and consumer user groups
on recommended equipment use.
The commission supports the use of state and national lawn and landscape
associations as sources of training and educational resources.
City of Galveston Public Works commented that improved traffic light coordination
could offset the emissions from the construction ban, lawn mowing ban, and
the 55 mph speed limit restriction.
The commission does not agree with this statement. The adopted rule will
result in an equivalent of approximately 4.6 tpd of NO
x
reduced. The new Division 9, Houston/Galveston Construction Equipment
Operating Restrictions; to Subchapter I, Non-road Engines; Chapter 114, Control
of Air Pollution from Motor Vehicles will result in an equivalent of 7.9 tpd
of NO
x
reduced. The SIP provision concerning
the 55 mph speed limit will provide 12.7 tpd of NO
x
emissions reductions. Improved traffic light coordination is a program
that is being adopted as a plan to lower emissions in the HGA. The commission
expects that the traffic light coordination measure will result in 0.8 tpd
of NO
x
emission reductions.
One individual commented that switching to electrically-powered lawn-care
equipment can have as great an impact as reduction vehicular traffic.
Lawn equipment emits approximately one tpd of NO
x
and 41 tpd of VOC emissions. The 2007 base case vehicular inventory
shows 258 tpd of NO
x
and 91 tpd of VOC. So, unless
a very high percentage of electrification of lawn and garden service equipment
is achieved, it is difficult to compare the effect of dealing with lawn care
equipment versus autos. Nevertheless, the emissions from lawn and garden service
equipment must be considered in adopting the emission reduction strategies
for HGA and the commission continues to believe that the adopted rules are
a necessary measure for a successful demonstration of attainment for HGA.
TSDA commented that this rule will limit the ability of dealers to service
spark-ignition engines 25 hp and under. TSDA, Wiccacon, and one individual
commented that this rule will not allow businesses to test and service equipment
before noon.
The commission agrees that any service or maintenance activities that require
the operation of small spark-ignition lawn and garden service equipment with
engines that are 25 hp or below is prohibited by the adopted rule. Service
activities that do not require operation of this equipment are not prohibited.
Dealers will be able to submit emission reduction plans that, if approved,
would enable them to operate the prohibited equipment during the morning hours.
TNLA, Harris Landscape, Lynn's, and one individual commented that manual
labor cannot be economically substituted for gasoline-powered equipment.
The commission does not believe that manual labor will have to be used
to substitute for gas- powered equipment. There are many other means which
operators of small, spark-ignition engines can conduct their operations. For
instance, electric equipment is a viable alternative to gasoline-powered equipment.
Furthermore, the commission believes that companies will be able to develop
approvable emission reduction plans that will allow them to continue their
services in a cost-effective manner. Given the number of years that companies
are being given to develop alternative means of supplying their services the
commission feels that there should be no disruption in the level or quality
of service.
REI, Harris County Judge Robert Eckels, and City of Houston Mayor Brown
commented that the rule is technically infeasible. REI commented that the
rule was proposed with less than a complete analysis of the economic feasibility.
CAP commented that the rule may be technically infeasible or unnecessarily
expensive. REI commented that the rule was proposed with less than a complete
analysis of the possible environmental or economic disbenefit. ExxonMobil
and BCCA commented that this rule exceeds federal mandates without proper
justification. ExxonMobil commented that the commission failed to provide
adequate scientific and technical justification, or economic analysis for
the proposed ban on the use of non-road equipment. ExxonMobil believes there
are technologically and economically feasible alternatives to the rules that
provide comparable environmental benefits at a much lower cost to the public.
TNLA commented that the nursery/landscape industry is a $14.8 billion industry
in Texas and that there are 2,300 landscape businesses affected by the proposed
SIP revisions. The sales volume is $1.5 billion annually. TNLA provided data
on the general profile of the industry: 56% sole proprietorships and 42% corporations;
general labor constitutes almost 57% of the workforce; supervisory foreman
make up 16% of the workforce; the average number of employees includes ten
general laborers, two in-house sales staff, three supervisors or foremen,
and one - two top management or owners; an average of nine employees per firm
had turfgrass maintenance responsibilities and spent an average of 68% of
their time performing those activities; the racial mix of employees statewide
was 58% Hispanic, 36% Caucasian, and 6% African-American; almost 40% of the
employees are between 21 and 30 years old; the pay scale is approximately
$45,000 for managers, $28,000 for supervisors, $12,000-14,000 for installation,
maintenance, or other types of labor, $17,000 for foremen and superintendents;
most firms supply their employees with safety items like glasses, back supports,
caps, shirts, gloves, and masks; 44% had sales of $100,000 or less while 24%
had sales of over $500,000; on average, a landscape firm in Texas shows a
11.5% profit margin; insurance is a major expense; equipment costs totaled
$32.5 million in 1993. Of this, vehicles represented 63% of the total with
22% for other equipment. On average, each landscape contractor spent approximately
$11,600 on new equipment for the year.
TNLA commented that the proposal is excessively onerous to the landscape
industry and disagreed with the commission statement that since the proposed
rules did not require additional controls or new equipment, there would not
be significant economic impacts to commercial operators beyond the shift in
the work schedule and possible implications caused by potential work delays.
TNLA noted that landscape equipment is generally replaced on a two- to four-year
cycle so landscape companies can adapt to regulations requiring new technology
as it becomes available with a minimal negative economic impact. The number
one cost for landscape companies is labor which is increasingly unavailable.
The industry is made up of very small, family owned businesses with narrow
profit margins. The business is very competitive with price being one of the
top two factors in selecting a landscape firm with service being second. Manual
labor cannot be substituted for the use of power equipment, for example, a
test in California showed that it took five times longer to clean a typical
landscape using a broom and rake than it would with a power blower. TAB commented
that the labor market is already suffering from shortages and many workers
might be forced to leave the industry to avoid the non-traditional work hours.
Bio Energy commented that the rule will cause the loss of employees who count
on the hours. RDC commented that if employers have to hire more personnel
to get the same amount of work done, employers will be forced to cut wages
or increase prices.
TSDA commented that the commission would be cutting their selling season
in half since the ban occurs during their top selling season. Frazier and
Air Cooled Engine Company commented that they are opposed to the rule as it
would greatly affect their business since it is a seasonal business and April
1 to October 31 includes the busiest part of their season and the busiest
part of the day. RDC commented that the ban would put an unfair economic burden
on the industry, both retail and wholesale business, along with the consumer
and commercial user. TNLA, Lynn's, and three individuals commented that the
time restrictions will leave less time to work and that will raise costs.
NASA commented that the proposal will result in increased grounds maintenance
costs as a result of a predicable decline in productivity due to asking workers
to work in the hottest part of the day. AAA commented that the rule will increase
costs related to lighting a job site and that this cost would be passed on
to the customer.
TSDA commented that the economic impact on dealers would be significant.
The average selling season for a dealer is between March and September. The
proposal would prevent dealers from doing business during this critical time
and would cut the selling season in half. The average dealer will lose an
average of $480.00 per day due to unbillable time and unrealized average parts
orders. This could be far more once overhead and other daily costs are added.
This could mean millions in lost revenue for dealers. Since the average dealer
usually sells between $100,000 and $500,000 gross, a loss of this type would
be catastrophic, it would mean the difference between keeping their business
open or going out of business. Mustang Mowing commented that their business
will not be able to meet demand. Dayton Pipe commented that it does business
with suppliers and customers who are outside of the HGA area and that a change
in their operating hours would hinder their ability to converse with these
suppliers or customers. Johnson Saw commented that the hours being restricted
are the most important to all lawn and garden dealers and users of this equipment.
The commission is aware of the economic and other difficulties this rule
will impose on businesses and individuals. In response to the comments the
commission has included an option for businesses to submit an emission reduction
plan that if approved would allow them the use of the prohibited equipment
in the morning hours. Further, the commission is adopting this rule with an
extended compliance schedule so that lawn and maintenance businesses may submit
an emissions reduction plan or supplement their equipment with electric-powered
units. The commission anticipates that affected companies will find and make
the necessary adjustments to minimize economic impacts, especially considering
the far more substantial impacts that would result from the failure of the
HGA area to attain federal air quality standards that this rule is designed
to help achieve. Although many of the rules included in the current SIP attainment
strategy will not be easy to implement and will cause many of the affected
entities to adjust normal operations, these rules are necessary in order to
demonstrate compliance with the ozone standard. As stated previously in this
preamble these rules are a necessary component of the HGA attainment strategy
and will achieve the equivalent effect of reductions in NO
x
of approximately 4.6 tpd.
The emission inventory maintained by the commission indicates that commercial
operations are the source of the majority of weekday emissions from lawn and
garden equipment. The commission cannot eliminate the operating restrictions
without an established, quantifiable, and enforceable replacement strategy
that demonstrates proven ozone reductions equivalent to those achieved by
these rules. The commission also cannot do away with the operating restrictions
because of the significant contribution that lawn and garden equipment makes
to the HGA area ozone levels. Because of this significant contribution that
the equipment affected by these rules make to the HGA area ozone levels, it
is essential that the equipment operating restrictions rules be implemented
along with the other rules and measures included in this SIP revision in order
for the HGA area to demonstrate attainment with the federal ozone standard.
The proposed rule contained an analysis of information available to the
commission regarding the costs and benefits of the proposed rule. The adopted
rules do not require additional control equipment or new technology; therefore
the commission believes that the rules are technically feasible. The commission
has worked extensively with lawn and garden industry and other affected industries
in the HGA area, along with consultants, to ensure that the emissions inventory
and the inventory of affected equipment in the area is as accurate and as
specific to the HGA area as possible. The accuracy of the inventories thereby
increases the accuracy of the modeling of the affected industries' contribution
to the air quality problem, as well as the necessary ozone reductions that
this rule is designed to achieve.
The commission continues to believe there will not be significant economic
impacts to commercial operators beyond the shift in work schedules and possible
implications caused by work delays. This information met the statutory requirements
of the TCAA and the APA because the information provided in the proposed rule
was sufficient for commenters to submit alternative assessments of the costs
and benefits.
Adequate notice is essential for fairness as well as a meaningful opportunity
to comment on a proposed rule.
United Loans, Inc.
v. Pettijohn
, 955 S.W.2d 649, 651 (Tex. App.-Austin 1997). To achieve
the goal of encouraging meaningful public participation in the formulation
and adoption of rules by state agencies, the notice must have sufficient information
so that interested persons can determine whether it is necessary for them
to participate in order to protect their legal rights and privileges. The
commission received comments which were substantial in both number and in
scope, regarding the costs of the proposed rule and the technical practicability
of compliance. The preamble for the proposed rules contained a discussion
of the FCAA requirements, including a detailed section by section discussion
of the rules. Although the commission did not have specific cost data available
at the time of proposal that could be included in the fiscal note, the proposal
preamble did include a discussion concerning costs to state and local governments,
the public benefit and the estimated costs for the affected sources, a small
and micro-business analysis, a draft RIA, a TIA, and a CMP consistency determination.
The commission received a number of comments that addressed multiple aspects
of the adopted rules, and has revised the rules in consideration of the cost
comments received. Therefore, the commission believes this goal has been achieved
and that the notice includes sufficient information to constitute adequate
notice.
The purpose of the comment period is for the public to provide the commission
with information to say why they agree or disagree. Some commenters stated
that the proposal did not meet the statute or that compliance with the proposed
rule is not technically or economically feasible. This broad comment does
not provide the commission with sufficient information to propose changes
or alternative strategies. There is no requirement that the commission determine
the probable economic cost of the unique aspects of every facility or source
that must comply, nor give the probable economic cost of every possible method
of control. The commission believes the proposed rule and preamble provided
enough information for commenters to rely on in order to submit specific comments.
Mere disagreement with cost or technical feasibility estimates does not render
notice inadequate. The commenters did not say how the notice is insufficient,
merely that it is insufficient. Nevertheless, the commission has reviewed
the proposed rule and preamble and has determined it is adequate because it
did identify those areas where those subject to the rule could expect to incur
costs.
BCCA, ExxonMobil, Phillips 66, and REI, stated that the proposed rules
did not include adequate notice as required under Texas Government Code, §2002.024.
The commenters stated that Texas Government Code, §2001.024, requires
adequate notice of a proposed rule, including information about its public
benefits and costs. The commenters stated that adequate notice is essential
for fairness as well as a meaningful opportunity to comment on a proposed
rule, and that courts have considered notice "adequate" only if: interested
persons can confront the agency's factual suppositions and policy preconceptions;
and the agency provides interested parties the opportunity to challenge the
underlying factual data relied upon by the agency. The commenters asserted
that in proposing the rules, the commission failed to provide interested parties
with sufficient information to constitute adequate notice.
The commenters stated that it has identified a number of critical gaps
in the underlying factual data, methodology, and analysis in support of the
proposed rules. The commenters asserted that the proposal included insufficient
information and analysis regarding costs and impacts. The commenters asserted
that the commission has not adequately responded to requests for additional
information from stakeholders. The commenters stated that the following requests
for information were outstanding: information regarding the modeling of emissions;
information regarding the corrected emissions inventory database; and information
supporting the estimated costs of control. However, available information
suggests that the commission dramatically underestimated the costs of the
proposed control strategies. This failure to provide the public with sufficient
information renders the notice of the plan inadequate. Section 2001.024 of
the APA requires the commission to provide sufficient information regarding
the Plan for public review and comment before adoption. The commenters stated
that this information is necessary in order to comment effectively on the
proposed rules and that data gaps in the proposal hindered effective comment.
The commission disagrees with the commenters and made no change in response
to these comments. Texas Government Code, §2001.024, requires of the
notice of a proposed rule include certain information. Texas Government Code,
2001.024(a)(5), requires that the notice state the public benefits expected
as a result of the adoption of the proposed rule and the probable economic
cost to persons required to comply with the rule. Adequate notice is essential
for fairness as well as a meaningful opportunity to comment on a proposed
rule.
United Loans, Inc. v. Pettijohn
, 955
S.W.2d 649, 651 (Tex. App.-Austin 1997). To achieve the goal of encouraging
meaningful public participation in the formulation and adoption of rules by
state agencies, the notice must have sufficient information so that interested
persons can determine whether it is necessary for them to participate in order
to protect their legal rights and privileges. The proposed rule contained
an analysis of information available to the commission regarding the costs
and benefits of the proposed rule. The commission received comments which
were substantial in both number and in scope, regarding the costs as well
as the benefits and in fact, revised the proposed rule in response to comments
concerning costs. As stated previously in this response to comments, the commission
believes this goal has been achieved and that the notice includes sufficient
information to constitute adequate notice.
The purpose of the comment period is for the public to provide the commission
with information to say why they agree or disagree. There is no requirement
that the commission determine the probable economic cost of the unique aspects
of every facility or source that must comply, nor give the probable economic
cost of every possible method of control.
The comments which state there are critical gaps did not identify what
those gaps are or how that results in inadequate notice. Mere disagreement
with cost estimates does not render notice inadequate.
The proposed rule meets the requirement to include sufficient information
by identifying those areas where persons subject to the rule could expect
to incur costs. To simply state that the proposal failed to provide sufficient
information does not provide the commission with sufficient information to
propose changes or alternative strategies. The commenters did not say how
the notice is insufficient, merely that it is insufficient. Nevertheless,
the commission has reviewed the notice and has determined it is adequate.
The commission is unaware of any requests for additional information to which
it was not completely responsive.
Phillips 66 stated that the commission has not provided a reasoned justification
for the proposal. The commenters asserted that a rule that would impose an
air emission abatement requirement that is not demonstrated to be practical
and economically feasible is directly contrary to the TCAA, §382.011(b),
and therefore is inconsistent with the Texas Government Code, §2001.033(a)(1)(B)
and §2001.035(c).
The commission has provided a "reasoned justification" for the rules in
this adoption package as required by Texas Government Code, §2001.033.
The requirement for a reasoned justification applies to the agency order finally
adopting a rule. The standard for compliance with the reasoned justification
requirement is substantial compliance, as determined by the legislature, which
amended the reasoned justification requirement in 1999. The commission has
provided the factual, policy and legal bases for the rule, as required. Texas
Government Code, §2001.024, requires only "a brief explanation" of the
rule upon proposal in addition to other elements such as the fiscal note and
public benefit evaluations. Both the rule proposal and adoption meet all of
the requirements of the APA.
BCCA, ExxonMobil, Phillips 66, and REI, stated that the proposed rules
did not include the local employment impact statement required under Texas
Government Code, §2001.022. The commenters stated that Texas Government
Code, §2001.022, requires the commission to determine whether the rule
proposal has the potential to affect a local economy before proposing the
rule for adoption. The commenters stated that if answered affirmatively, the
commission must request that the Texas Employment Commission to prepare a
local employment impact statement describing in detail the probable effect
of the rule on employment in each geographic area affected by the rule for
each year of the first five years that the rule will be in effect. The commenters
further asserted that the commission failed to make the required initial determination
and ignored the potential for the proposal to adversely affect the local economy.
The commenters stated that a local employment impact statement should have
been requested and prepared in advance of the proposal.
The commission agrees with the commenters that the proposed rule may affect
a local economy, however, does not agree that it is the responsibility of
the commission to provide the local employment impact analysis. The APA requires
state agencies to determine whether a rule may affect a local economy before
proposing a rule for adoption. If the agency determines that a proposed rule
may affect a local economy, the agency must send a copy of the proposed rule
and other information to the Texas Workforce Commission (Workforce Commission)
before the agency files notice of the proposed rule with the secretary of
state. The APA requires the Workforce Commission to prepare a local employment
impact statement for proposed rules, if a state agency requests the statement.
The commission determined that the proposed rule might affect a local economy,
and sent the proposed rule and other requested information to the Workforce
Commission. The commission received a letter from the Workforce Commission,
indicating that the Workforce Commission did not have the ability to determine
the potential local employment impacts from the proposed rule.
BCCA, ExxonMobil, Phillips 66, and REI stated that the proposed rules did
not include an adequate TIA as required under Texas Government Code, §2007.
The commenters stated that the TIA provision mandates that covered agencies
"take a 'hard look' at the private real property implications of the actions
they undertake...," according to the Office of the Attorney General,
The commenters stated that agencies must also comply with guidelines developed
by the Texas Attorney General when developing the TIA and that according to
these guidelines, agencies must carefully review governmental actions that
have a significant impact on the owner's economic interest. The commenters
stated that these guidelines include the statement: "Although a reduction
in property value alone may not be a 'taking,' a severe reduction in property
value often indicates a reduction or elimination of reasonably profitable
uses." (21 TexReg 392, January 12, 1996). The commenters stated that examples
of aspects of the rule proposal that could significantly impact private real
property in a manner that constitutes a taking include gas-fired compressor
engines and other point source NO
x
controls.
The commenters stated that the commission provided the public no basis
to infer that a cost/benefit analysis or a reasonableness determination was,
in fact, performed as necessary to support the TIA exemption claim because
the preamble contains only the bare assertions. The commenters asserted that
the proposed rules will impose a greater burden than is necessary, and are
not reasonably taken to fulfill a federal mandate. The commenters commented
that according to the Attorney General's Guidelines, a full TIA was required
to be completed with the proposal, and that failure to perform a TIA could
invalidate the rules.
The primary reason the commission determined that this rule did not constitute
a takings under Texas Government Code, Chapter 2007 is that it will not burden
private real property. This rule applies to non-road equipment which is not
real property or appurtenance thereto. The commission believes the adopted
rules are exempt under §2007.003(b)(4) because they are reasonably taken
to fulfill an obligation mandated by federal law. While several governmental
actions are subject to being reviewed under Chapter 2007, including the adoption
of rules, §2007.003(b)(4) specifically excludes an action that is reasonably
taken to fulfill an obligation mandated by federal law. The rules are adopted
to meet the air quality standards established under federal law as NAAQS.
The commission also believes that the adopted rules meet an additional
exception to the requirements of Texas Government Code, Chapter 2007. First,
Texas Government Code, §2007.003(b)(13), states that Chapter 2007 does
not apply to an action that: 1) is taken in response to a real and substantial
threat to public health and safety; 2) is designed to significantly advance
the health and safety purpose; and 3) does not impose a greater burden than
is necessary to achieve the health and safety purpose. Although the rule revisions
do not directly prevent a nuisance or prevent an immediate threat to life
or property, they do prevent a real and substantial threat to public health
and safety and significantly advance the health and safety purpose. This action
is taken in response to the HGA area exceeding the federal ambient air quality
standard for ground-level ozone, which adversely affects public health, primarily
through irritation of the lungs. The action significantly advances the health
and safety purpose by reducing ambient VOC and ozone levels in HGA. Consequently,
these rules meet the exemption in §2007.003(b)(13).
The commission has included elsewhere in this preamble its reasoned justification
for adopting this strategy and has explained why it is a necessary component
of the SIP, which is federally mandated. This discussion, as well as the HGA
SIP which is being adopted concurrently, explains in detail that every rule
in the HGA SIP package is necessary and that none of the reductions in those
packages represent more than is necessary to bring the area into attainment
with the NAAQS. This rulemaking therefore meets the requirements of Texas
Government Code, §2007.003(b)(4) and (13). For these reasons the rules
do not constitute a takings under Chapter 2007 and do not require additional
analysis.
ExxonMobil, BCCA, Phillips 66, and REI stated that the proposed rules did
not include an adequate small business and micro-business assessment as required
under Texas Government Code, §2006.002. BCCA also commented that none
of these assessments applied the mandated cost comparison standards. The commenters
stated that an analysis of the costs of compliance for small and micro-businesses
must also compare the costs of compliance for these businesses with the costs
for the largest businesses affected by the rule. The commenters stated that
the comparison must use at least one of the following standards: cost for
each employee, cost for each hour of labor, or cost for each $100 of sales.
The commenters asserted that the rule proposal failed to include the mandated
cost comparison standards. The commenters stated that this is the case even
in those instances where the commission acknowledged a significant impact.
The commenters stated that the commission either restated the costs of compliance
it identified in the analysis of public benefits and costs, or concluded that
it cannot determine the cost to small businesses.
The commenters asserted that the rule proposal assessments fall short of
what Texas law requires and that it is not sufficient for the agency merely
to state that the costs for small and large businesses will be the same. The
commenters stated that the rationale behind requiring a comparison using an
established standard (e.g., cost for each employee, cost for each hour of
labor, or cost for each $100 of sales) is to determine whether there is a
disparate impact on small businesses. The commenters stated that according
to
Unified Loans v. Pettijohn
, 955 S.W.2d
at 652 (Court of Appeals -- Austin, 1997), the statute's purpose is to obtain
"an objective assessment of the agency's proposed action by forcing it to
consider seriously. . . the effect of the rule on small businesses, including
an analysis of their costs of (compliance) and a comparison of their costs
with the cost of compliance for the largest businesses affected. ..." The
commenters stated further that the commission cannot merely conclude that
the costs to small businesses "cannot be determined," and is obliged to include
in the notice "some basis" for its conclusion so that interested parties can
"confront that basis in a meaningful way in their comments." (
Unified Loans v. Pettijohn
, 955 S.W.2d at 653.)
The commenters stated that in the rule proposal preamble, the commission
did not publish the information mandated by Texas law and that as a result,
it is impossible for the public to comment on whether the agency adequately
considered the effect of the rule on small businesses, thus rendering the
notice of the plan inadequate. The commenters stated that Texas Government
Code, §2006.002, requires the commission to provide a comparison of the
proposed rule's impact on small and large businesses, using the specified
standards, for public review and comment before adoption.
TNLA commented that the proposal is excessively onerous to the landscape
industry and disagreed with the commission statement that since the proposed
rules did not require additional controls or new equipment, there would not
be significant economic impacts to commercial operators beyond the shift in
the work schedule and possible implications caused by potential work delays.
TNLA noted that landscape equipment is generally replaced on a two- to four-year
cycle so landscape companies can adapt to regulations requiring new technology
as it becomes available with a minimal negative economic impact. The number
one cost for landscape companies is labor which is increasingly unavailable.
This regulation hits the industry directly where it is most vulnerable and
creates the worst economic impact by not allowing any alternatives. The industry
is made up of very small, family owned businesses with narrow profit margins.
The business is very competitive with price being one of the top two factors
in selecting a landscape firm with service being second. Manual labor cannot
be substituted for the use of power equipment, for example, a test in California
showed that it took five times longer to clean a typical landscape using a
broom and rake than it would with a power blower. TAB commented that the labor
market is already suffering from shortages and many workers might be forced
to leave the industry to avoid the non-traditional work hours. Bio Energy
commented that the rule will cause the loss of employees who count on the
hours. RDC commented that if employers have to hire more personnel to get
the same amount of work done, employers will be forced to cut wages or increase
prices.
The proposal preamble acknowledged that there may be fiscal implications
for small or micro- businesses as a result of the adoption and enforcement
of the rules. Although the commission did not have information about number
of employees, hours of labor, or amount of sales income the assessment did
state that the economic impacts were not anticipated to be significant and
that they were not anticipated to extend beyond any impact due to the shift
in work schedules and possible implications from work delays. The commission
did state that additional employees might have to be hired or additional equipment
might be purchased. Adequate notice is essential for fairness as well as a
meaningful opportunity to comment on a proposed rule.
United Loans, Inc. v. Pettijohn
, 955 S.W.2d 649, 651 (Tex. App.-Austin
1997). To achieve the goal of encouraging meaningful public participation
in the formulation and adoption of rules by state agencies, the notice must
have sufficient information so that interested persons can determine whether
it is necessary for them to participate in order to protect their legal rights
and privileges. The proposed rule contained an analysis of information available
to the commission regarding the costs and benefits of the proposed rule. The
commission believes that the analysis in the proposal did provide a basis
for the submission of comments and the commission received a substantial number
of comments related to small businesses. These included comments stating that
equipment for commercial lawn and garden operations is replaced regularly
on a two- to four-year cycle. For example, this would allow operators to replace
a substantial portion of their current inventory with electric equipment prior
to the 2005 rule implementation date. Based on this information, the commission
believes that capital expenditures resulting from commercial operators' compliance
with the modified rule are within the normal replacement schedule of their
equipment. For example, replacement of existing inventories with electric
equipment will allow commercial operators to continue their operations in
the morning hours. The commission believes that replacement of equipment could
allow commercial operations to continue to operate with the same number of
employees after the 2005 implementation date. Further, additional comments
indicate that the primary expense for these businesses is labor. The adopted
rule allows commercial operators and persons to submit emission reduction
plans by May 31, 2003, for approval by the executive director and the EPA
no later than May 31, 2004. If an acceptable plan is submitted, commercial
operators and persons will exempt from operating hour restrictions upon implementation
of these rules in 2005 and therefore, and will be able to operate during the
restricted hours. This would also eliminate or reduce the need for increased
labor costs. The executive director may allow plans to be submitted after
May 31, 2003. In any event, a plan must be approved prior to the use of that
plan for compliance with the requirements of this division.
The commission believes that the information provided in the proposal was
sufficient to provide a basis for comments on the impacts of the adopted rules
on small and micro-businesses. In response to these comments, the commission
has modified the proposal and is adopting a rule that will mitigate the effects
on small and micro-business commercial operators.
BCCA, ExxonMobil, Lynn's, OPEI, Phillips 66, REI, TNLA, and one individual
commented on the draft RIA and stated that the proposed rules were not evaluated
in accordance width the analysis requirements for a major environmental rule.
EWI commented that this rule does not meet the definition of a major environmental
rule. The commenters stated that Texas Government Code, §2001.0225, requires
an RIA for certain major environmental rules. The commenters stated that the
commission must consider the benefits and costs of the proposed rule in relationship
to state agencies, local governments, the public, the regulated community,
and the environment. The commenters stated further that the commission must
also incorporate aspects of this analysis into the fiscal note in the proposed
rules (e.g., identify the costs and the benefits; describe reasonable alternative
methods for achieving the purpose of the rule considered by the agency; provide
the reasons for rejecting those alternatives; and identify the data and methodology
used in performing the analysis). The commenters stated that under §2001.0225(d),
the commission must also find that "compared to the alternative proposals
considered and rejected, the rule will result in the best combination of effectiveness
in obtaining the desired results and of economic costs not materially greater
than the costs of any alternative regulatory method considered."
The commenters stated that the rule proposal preamble statement that the
rules are exempt from the RIA requirement because federal law mandates the
rules is a legally flawed effort to avoid an RIA and may render the rules
invalid. The commenters stated that federal law does not mandate the control
requirements, emission rates, and use restrictions contained in the proposal
and asserted that many of the proposed rules exceed specific federal rules
and standards applicable to the same sources. The commenters stated that examples
of departures from the federal framework include the following: boiler, turbine,
and other fired equipment emission limits set well below federal new source
performance standards (NSPS), reasonably available control technology, best
available control technology (BACT), or lowest achievable emission rate (LAER)
limits for the same sources; and compressor engine emission limits set at
unprecedented low levels specifically designed to be unachievable and prevent
the further use of the affected engines.
TNLA commented that while the commission is required to reduce emissions,
the specific action of banning use of equipment is not required. TNLA argues
that an impact study of projected costs ad benefits of the regulations is
necessary. OPEI notes that the draft RIA states that the specific SIP measures
are not generally required by the FCAA, but instead, the FCAA provides states
with flexibility to develop SIPs that will achieve air quality standards.
Based on this, the commission contends that the proposed morning ban is exempt
from the RIA requirements because they are required by federal law. OPEI asks
if the commission has confirmed its interpretation of the RIA requirements
with either the authors of SB 633 or the State Attorney General, and whether
the commission's RIA interpretation is currently subject to legal challenge.
OPEI also wanted to know the criteria the commission applies to distinguish
major from non-major rules and the basis through which the commission has
determined the proposed ban falls into the non-major category.
ExxonMobil commented that simply saying that federal law requires the rules
does not make it so. ExxonMobil stated that federal law, for instance, did
not mandate a 90% reduction in emissions from stationary sources of NO
The commission does not agree that the adopted rules meet the definition
of a major environmental rule, or that the commission's interpretation of
the exemption for federally mandated standards is legally flawed. The Texas
Government Code, §2001.0225, only applies to a major environmental rule
adopted by a state agency, the result of which is to: 1) exceed a standard
set by federal law, unless the rule is specifically required by state law;
2) exceed an express requirement of state law, unless the rule is specifically
required by federal law; 3) exceed a requirement of a delegation agreement
or contract between the state and an agency or representative of the federal
government to implement a state and federal program; or 4) adopt a rule solely
under the general powers of the agency instead of under a specific state law.
This rulemaking action does not meet any of these four applicability requirements,
and is adopted in substantial compliance with the RIA requirements. Texas
Government Code, §2001.035. Further, the adopted rules are also intended
to obtain NO
x
and VOC emission reductions which
will result in reductions in ozone formation in the HGA ozone nonattainment
area under 42 USC, §7409. These rules are intended to implement an operating-use
restriction program requiring that lawn and garden service equipment powered
by spark-ignition engines, 25 hp or below utilized by commercial operators,
or for uses not exempt under §114.452(b), are restricted from use between
the hours of 6:00 a.m. and noon, April 1 through October 31. This program
is part of the strategy to reduce the formation of ozone by delaying NO
This conclusion is supported by the legislative history for Texas Government
Code, §2001.0225. During the 75th Legislative Session, SB 633 amended
the Texas Government Code to require agencies to perform an RIA of certain
rules. The intent of SB 633 was to require agencies to conduct an RIA of major
environmental rules that will have a material adverse impact, and will exceed
a requirement of state law, federal law, or a delegated federal program, or
are adopted solely under the general powers of the agency. The commission
provided a cost estimate for SB 633 that concluded "based on an assessment
of rules adopted by the agency in the past, it is not anticipated that the
bill will have significant fiscal implications for the agency due to its limited
application." The commission also noted that the number of rules that would
require assessment under the provisions of the bill was not large. Because
of the ongoing need to address nonattainment demonstrations required by federal
law, the commission routinely proposes and adopts SIP rules. If each rule
proposed for inclusion in the SIP was incorrectly considered as exceeding
federal law, every SIP rule would require the full RIA contemplated by SB
633. This result would be inconsistent with the cost estimates and fiscal
notes prepared by the commission and by the LBB. Since the legislature is
presumed to understand the fiscal impacts of the bills it passes, and that
presumption is based on information provided by state agencies and the LBB,
the commission believes that the intent of SB 633 was only to require the
full RIA for rules that meet the requirements under §2001.0225(a). While
the SIP rules will have a broad impact, that impact is no greater than is
necessary or appropriate to meet the requirements of the FCAA. In other words,
the adopted rules are intended to meet federal and state law, and do not go
above and beyond what is required to meet federal or state statutes.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
It is presumed that "when an agency interpretation is in effect at the time
the legislature amends the laws without making substantial change in the statute,
the legislature is deemed to have accepted the agency's interpretation."
The commission's interpretation of the RIA requirements is also supported
by a change made to the APA by the legislature in 1999. In an attempt to limit
the number of rule challenges based upon APA requirements, the legislature
clarified that state agencies are required to meet these sections of the APA
against the standard of "substantial compliance." Texas Government Code, §2001.035.
The legislature specifically identified Texas Government Code, §2001.0225
as falling under this standard. The commission has substantially complied
with the requirements of §2001.0225.
Currently, several lawsuits have been filed that challenge rules adopted
by the commission with regard to the RIA requirements. The commission, through
the Texas Attorney General's office, has argued that it is not required to
prepare a full RIA if the proposed rule is not a major environmental rule
that exceeds any of the four applicability requirements of Texas Government
Code, 2001.0225. A "major environmental rule" means a rule with the specific
intent to protect the environment or reduce risks to human health from environmental
exposure and that may adversely affect in a material way the economy, a sector
of the economy, productivity, competition, jobs, the environment, or the public
health and safety of the state or a sector of the state. When determining
whether a proposed rule is a major environmental rule, the commission must
consider the two prongs of the definition of "major environmental rule." First,
the commission must determine the specific intent of the rule. In this case,
the concept of shifting NO
x
and VOC emissions
to the afternoon will help reduce the formation of ozone. The HGA area exceeds
the federal ambient air quality standard for ground-level ozone, which adversely
affects public health, primarily through irritation of the lungs. Thus, the
adopted rules will reduce risks to human health from environmental exposure.
Second, the commission must determine if the proposed rules will have an adverse,
material effect on the economy, a sector of the economy, productivity, competition,
jobs, the environment, or the public health and safety of the state or a sector
of the state. The commission considers the results of the fiscal analysis
that is required for every proposed rule by the APA, as well as information
that is generally available to the commission about an affected industry.
For these rules, the commission focused on whether or not the work delay would
affect a sector of the economy in an adverse material way. The commission
stated in the proposal that it did not believe that businesses that provide
lawn and garden services comprise a sector of the economy or that the rules
would have the adverse, material affect contemplated by §2001.0225.
Further, the commission does not believe that the rules will adversely
affect in a material way, the economy, productivity, competition, jobs, the
environment, or the public health and safety of the state or a sector of the
state, particularly since the adopted rule allows commercial operators to
submit emission reduction plans that, if approved, will enable them to operate
during the prohibited hours. Productivity and jobs should not be adversely
affected since the option to submit an emission reduction plan, coupled with
the expected natural turnover of lawn and garden equipment will enable most
commercial operators to continue in their normal course of business. The rule
should not adversely affect public health and safety since it is intended
to reduce ozone. Further, the exclusions for domestic and emergency use and
the option to submit an emission reduction plan will reduce the need to perform
lawn and garden services in the afternoon or early evening hours.
Therefore in addition to not exceeding an express standard set by federal
law, these rules do not exceed state requirements, and are not adopted solely
under the general powers of the agency because the provisions of the TCAA, §§382.011,
382.012, 382.017, 382.019, and 382.039, authorize the commission to implement
a plan for the control of the states air quality, including measures necessary
to meet federal requirements. The remaining applicability criteria, pertaining
to exceeding a delegation agreement or contract between the state and the
federal government does not apply. Thus, the commission is not required to
conduct a regulatory analysis as provided in Texas Government Code, §2001.0225.
OPEI commented that Texas would receive greater SIP emission reduction
credits through the mandated sale in Texas of spill-proof, portable gasoline
containers. TNLA, BCCA, TLS, PPEMA, EWI, Spring Valley, Lynn's, Cornelius,
Harris Landscape, Poulan, and two individuals suggested that the commission
adopt California's spill-proof container. PPEMA suggested that in the event
the commission falls short of the emission goals for HGA, even after accounting
for the EPA's Phase II regulations, the commission should evaluate the effect
of potential control measures to address spillage and refueling emissions
from lawn and garden equipment. Friendly Robotics commented that they respectfully
disagree with OPEI in its endorsement of a "no-spill" gasoline container rule
(a rule that OPEI would like to substitute for the lawn mowing time shift
rule) siting the fact that the "no-spill" containers are being offered as
an alternative so as to remove focus from "the devices that actually burn
the gasoline and spew out the emissions, . . ." (i.e., internal combustion
engines).
The commission has not had the opportunity to extensively analyze the data
submitted that supports the implementation of the California spill-proof container
regulation. However, the commission does not believe that the spill-proof
container rule would result in emission reductions that would have the same
ozone reduction benefit as the lawn and garden rules. Even if the commission
continues to review this data, the commission is unable to adopt a rule of
this nature at this time and believes that it is necessary to adopt the lawn
and garden shift rules.
OPEI claims that the HGAC estimates that the population in the affected
eight-county non- attainment area in 2007 will be 5.14 million people, which
is roughly 15% of the 33.5 million people that the CARB evaluated. Second,
OPEI claims that 15% of 9.8 million gasoline containers (CARB's estimate)
results in roughly 1.5 million portable gas containers in the HGA area. Third,
they claim that if those 1.5 million containers were replaced with spill-proof
containers in cooler California, it would result in a reduction of roughly
13 tpd in the HGA area (15% of 87 tpd CARB's container emissions contribution).
Fourth, OPEI claims that the rate of evaporative emissions is very dependent
on temperature and gasoline vapor pressure. OPEI assumes that the average
summer temperature in Texas is around 15 degrees hotter than California, and
that the EPA methodology indicates that the average rate of evaporative emissions
in Texas is roughly 30% higher than the rate of evaporative emissions from
containers in California (simply accounting for temperature alone assuming
fuel vapor pressure is the same). OPEI asserts that according to CARB's calculations,
evaporative emissions constitute roughly 75% of container emissions or roughly
9.75 tpd of projected reactive organic gas (ROG) emissions from gasoline containers
in the HGA. Thus, OPEI states that the much higher summer temperatures in
Texas would result in a higher evaporation rate than California resulting
in an additional 2.93 tpd (30% x 9.75) of ROGs in Houston. OPEI believes that
applying the CARB principles to the HGA population (with an adjustment for
higher temperatures) would result in a total emission contribution from spill-proof
containers in 2007 of 15.93 tons of ROGs per day (13 "California-based" tons
plus 2.93 "added Texas heat" tons). OPEI assumes then that because spill-
proof containers will reduce container emissions by 73%, a container rule
will reduce year 2007 emissions in the HGA by 11.63 tons of ROGs (73% x 15.93).
The commission disagrees with the conclusions of OPEI. OPEI relies on population
estimates that have not been confirmed by the commission. OPEI also relies
on data gathered from California which cannot be applied to the HGA. For instance,
OPEI estimates that 1.5 million gasoline containers are present in the HGA.
However, this data is based on assumptions made by the CARB about gasoline
container populations across that entire state. OPEI also assumes that California
is 15 degrees cooler than Texas. This has not been verified by the commission
and/or the EPA. The commission would need to determine what information this
assumption was based on before making adjustments to the inventory. For instance,
was this information based on mean state-wide temperatures? What is the source
of the temperature data? Does this differential apply to Houston, whose summertime
temperatures are moderated by the Gulf of Mexico, etc.? As for evaporative
emissions constituting roughly 75% of container emissions, or roughly 9.75
tpd, the commission has received no information concerning how these figures
were determined. The commission would again need to determine on what information
these assumptions were based. OPEI also contends that a gas can rule would
result in full compliance/turnover by 2007, since the average portable container
has a useful life of five years. If the average useful lifetime of fuel containers
is five years, then the commission would expect that only half of the containers
could continue in use well beyond five years. A significant number of older
containers could continue in use well beyond five years. OPEI contends that
the commission would ultimately receive from the EPA at least comparable (if
not greater) SIP emission reduction credits from a spill-proof container rule
in lieu of the proposed ban. Even if it can be shown that the no-spill container
rule will reduce hydrocarbon emissions in an amount equal to or greater than
the amount shifted, there is no guarantee that equivalent ozone benefits would
be realized. Lawn and garden emissions (which include NO
x
as well as VOC) in the morning are particularly important to afternoon
ozone formation, and a significant amount of morning emissions would continue
to occur even with all the inventory modifications suggested in the comments,
including the proposed gas can rule.
OPEI commented that there were flawed and exaggerated projected inventory
contributions associated with lawn and garden engine exhaust. They suggested
re-running the emission inventory model with corrected assumptions that the
OPEI assumes the commission will receive from the EPA via a spill-proof container
rule. OPEI believes that these inventory corrections will reduce the EPA-
approved SIP credits resulting from the proposed ban to around four tpd of
VOC. OPEI commented that a spill-proof container rule will improve water quality
(by removing spills associated with personal water craft) and improve overall
fuel efficiencies. They also commented that a spill-proof container rule would
be supported (rather than challenged) by all affected industries (including
Texas commercial landscape companies that would save money through not wasting
fuel and container manufacturers that would sell their new products). OPEI
commented that if the commission adopted a spill-proof container rule on a
state-wide basis, then the entire state would receive dramatically greater
SIP credits. OPEI commented that if the commission cannot implement a spill-proof
container rule, then it will lose credibility with all of the other industries
that were requested to develop superior alternatives.
The commission disagrees with this comment. The commission does not believe
the projected inventory was flawed or exaggerated. The commission does not
believe it is appropriate or accurate to adjust the HGA inventory using assumptions
based on California data until that data has been demonstrated to be applicable
to the HGA area and approved by the commission and EPA. The commission acknowledges
that the no-spill container rule may have a number of benefits beyond the
reduction of VOCs. The commission has not had the opportunity to extensively
analyze the California data; however, the commission does not believe that
the spill-proof container rule would result in emission reductions that would
have the same ozone reduction benefit as the lawn and garden rules. The commission
analyzed where emission reduction measures are most needed and where emission
reduction measures will be most effective in order to demonstrate attainment.
Even if the commission continues to review this data, the commission is unable
to adopt a rule of this nature at this time and believes that it is necessary
to adopt the lawn and garden shift rules.
OPEI commented that the commission apparently relied on the Spring 1999
EPA Non-Road Engine Model and that this model fails to recognize significant
reductions in "deterioration rates" from the new EPA Phase II compliant handheld
and non-handheld equipment.
The commission disagrees with this comment. The commission utilized the
latest version of the NONROAD model. This means that the model did not fail
to recognize significant reductions in "deterioration rates" from the new
EPA Phase II compliant handheld and non-handheld equipment.
TNLA, Harris Landscape, TSDA, Lynn's, OPEI, PPEMA, RDC, Briggs & Stratton,
Poulan, EETC, and three individuals commented that they believe the commission's
emission reductions do not seem to take full credit for the two phases of
federal emission standards for small spark-ignition engines that have already
taken effect. Hence, the commenters argue that lawn equipment will be much
cleaner than the commission projects. TNLA commented that the proposal fails
to recognize the regulation of gasoline powered lawn and garden equipment
being phased in by the EPA. According to a TNLA survey, most such equipment
is replaced on a no more than four-year cycle with the majority being replaced
on a two-year cycle. By 2005, the equipment on which the commission modeling
is based will no longer be used by commercial firms. EPA exhaust emission
regulations, Phase I, effective model year 1997, reduced emissions by 30%
from unregulated levels. The Phase II regulations call for a 78% reduction
from the Phase I levels. PPEMA added that the EPA Phase II rules will provide
sufficient reductions for the commission to reach the targeted reductions
and thus there is no need for the proposed rule. TSDA suggested giving the
CARB Tier I and II standards a chance to work before implementing a ban on
small engine use.
The commission disagrees with this statement. The lawn equipment modeling
did take into account the various federal regulations affecting small engines
which are being phased in over the next several years. The modeling also accounted
for fleet turnover, i.e., the replacement of older equipment with cleaner
new equipment.
Baker Botts commented that it generally supports the ongoing efforts by
the commission to develop a SIP that is technologically achievable, economically
reasonable, and legally approvable. Baker Botts, BCCA, ExxonMobil, Harris
County Judge Robert Eckels, Phillips 66, Spring Valley, and an individual
commented that the commission should incorporate into the SIP a greater level
of reductions from federally preempted sources and stated that EPA-regulated
sources account for about 40% of the NO
x
emissions
in the HGA. The commenters stated that the EPA issued a number of regulations
for some federally preempted sources, such as land-based spark engines, marine,
recreational and land-based diesel engines, aircraft and locomotive engines,
well after the FCAA deadlines, and that the EPA recently strengthened rules
for on-road and non-road vehicles and fuels, such as low sulfur gas and diesel,
Tier II motor vehicles, heavy-duty highway vehicle standards, and non-road
Tier II/Tier III heavy-duty engine standards. The commenters stated that delays
in implementing these rules have prompted the commission to propose technically
and economically infeasible emission reductions from sources in HGA that the
state has authority to regulate to make up for the missing federal reductions.
The commenters stated that these delays have forced the commission to propose
expensive regional fuels and significant use restriction regulations. The
commenters stated that the commission and the EPA can ensure an equitable
distribution of the compliance burdens necessary to meet mandated air quality
improvement in HGA only by allowing the SIP to capture anticipated emission
reductions from federally preempted sources. Baker Botts noted that the EPA
demonstrated a willingness to assume responsibility for a portion of emission
reductions by creating a process in Los Angeles called a "public consultative
process," that would resolve issues related to emissions from national and
international sources, and that the EPA has also provided flexibility in obtaining
offsets by allowing states to provide offsets to refiners based on emission
reductions that the EPA projected would result from mobile sources using Tier
II gasoline. Baker Botts suggested that this same sort of prospective crediting
should be used to develop a more rational HGA SIP, and that the EPA should
allow the commission to credit in the SIP the prospective emission reductions
that will result from implementation of the Tier II gasoline rule and from
other federally preempted sources. Finally, Baker Botts cited two cases wherein
the District of Columbia Circuit has approved the EPA's flexibility with respect
to statutory deadlines under the FCAA when the EPA has failed to meets its
own deadlines, and this failure was deemed to upset the balanced federal/state
responsibilities under the FCAA. ExxonMobil commented that it supports the
commission and the EPA crediting the HGA SIP with an additional 60 tpd of
federally preempted emission reductions that will occur over the next ten
years. Harris County Judge Robert Eckels commented that the commission should
work with the EPA to accelerate the implementation schedule for federally
preempted emissions so that at least one-half of the related emission reductions
are achieved by 2007, and that as a part of this process, the commission should
delineate federal assignments detailing the engine standards and emission
reductions necessary to achieve real and sustainable pollution reductions.
The commission agrees with the commenters that emission reductions from
federally preempted sources would provide benefits for the HGA SIP demonstration,
and the inability of the commission to regulate certain source categories
has necessitated the use of other ozone control strategies. However, the commission
understands that the EPA SIP approval process does not provide a mechanism
for credit for emission reductions that occur after the attainment date. The
commission understands that EPA is not currently considering accelerating
implementation schedules for existing federal rules. The commission is working
with EPA to determine the availability of SIP credit for many non-traditional
control strategy mechanisms, like economic incentive programs and flexibility
for preempted source categories. Additionally, the commission is working with
EPA to determine an appropriate federal contribution credit available for
the HGA SIP.
OPEI commented that the proposed use ban would not result in any significant
environmental benefits that would justify its substantial adverse impact on
the health and the jobs of thousands of landscapers and gardeners as well
as the economic viability of hundreds of landscaping and gardening businesses.
The commission disagrees with this statement. The commission recognizes
that compliance with this rule may cause unavoidable productivity (economic)
losses in the HGA. However, the commission anticipates that commercial operators
will find and make the necessary adjustments to minimize these impacts, especially
considering the far more substantial impacts that would result from the failure
of the HGA to attain federal air quality standards that this rule is designed
to help achieve. Although many of the rules included in the current SIP attainment
strategy will not be easy to implement and will cause many of the affected
entities to adjust normal operations and make certain sacrifices, these rules
are of critical importance in the protection of the environment and human
health, which is essential for continued economic prosperity. If adopted,
this rule will result in the equivalent of approximately 4.6 tpd of NO
OPEI commented that the commission's rule will at most shift approximately
30.6 tpd in exhaust emissions and will not impact evaporative diurnal and
spillage emissions from portable gasoline containers.
Even if it can be shown that the proposed gas can rule will reduce hydrocarbon
emissions in an amount equal to or greater than the amount shifted in the
commission rules, there is no guarantee that equivalent ozone benefits would
be realized. Small, spark-ignition engine emissions (which include NO
OPEI commented that the commission used the default non-road growth assumptions
to project future activity levels in the HGA. OPEI also commented that current
EPA Non-Road Model apparently applies an annual growth rate of 2.4%. However,
OPEI believes that there has been relatively no growth in the population of
lawn and garden equipment over the last decade, and that the commission has
therefore overestimated emissions from this equipment. OPEI therefore requests
that the commission apply a growth factor of 1%.
The commission estimated growth based on projections of human population,
which is indeed lower than the default non-road projections. As for the use
of a 1% growth rate, the commission and the EPA would require documentation
of how this growth rate was derived before using it to model future emissions.
Montgomery County commented that the commission did not provide the predicted
reductions of NO
x
and VOC emissions.
The commission disagrees with this statement. This data was provided in
the preamble of the rule package. It was stated that these rules will result
0.58 tpd NO
x
shifted, 20.6 tpd VOC shifted, which
will lead to a 7.7 tpd NO
x
reduction equivalent.
These numbers have been subsequently revised to 0.23 tpd NO
x
shifted and 12.4 tpd of VOC shifted resulting in a reduction in ozone
that is equal to approximately 4.6 tpd NO
x
reduction.
EPA commented that for approvability the state should provide further documentation
of how the benefits of this measure were calculated as this is primarily a
VOC measure that has been assigned a NO
x
reduction
of 7.7 tpd.
This rule is intended to reduce the formation of ozone and accomplishes
this by shifting VOC and NO
x
emissions later
into the day allowing less reaction time with sunlight. EPA is correct that
the rule shifts more VOC than NO
x
and could be
seen as primarily a VOC measure. The commission characterization of the rules
results from the fact that they results in an ozone reduction equivalent to
a NO
x
reduction of approximately 4.6 tpd. This
figure is a modification of the original 7.7 tpd estimate that appeared in
the proposal. Documentation and explanation of these calculations is provided
in the SIP narrative that is concurrently adopted with this rule.
TNLA, Harris Landscape, and Lynn's commented that the data and modeling
that the rule is based on are flawed because of an incomplete non-road inventory,
local meteorology, use of national data not applicable to the HGA, and a lack
of conclusive studies regarding ozone formation.
The commission disagrees with these comments. The commission has worked
extensively with lawn and garden industry and other affected industries in
the HGA area, along with consultants, to ensure that the emissions inventory
and the inventory of affected equipment in the area is as accurate and as
specific to the HGA area as possible. The accuracy of the inventories thereby
ensures the accuracy of the modeling of the affected industries' contribution
to the air quality problem, as well as the necessary ozone reductions that
this rule is designed to achieve. The commission is required to use a federally-recognized
and approved model for developing data that will be used to demonstrate attainment
with the SIP. The commission used state-of-the-art photochemical methodologies
to develop this rule. The Comprehensive Air Model with Extensions model that
was used is the latest version of the photochemical model recognized by the
EPA for SIP modeling. Previous inventories had been supplied by the EPA in
their "Non-Road Equipment and Vehicle Emission Study" (NEVES, EPA-21A- 2001,
November 1991). As such, the accepted method to model years other than the
1990 NEVES data was to apply growth factors from the Economic Growth Assessment
System (EGAS). Over the last year, however, a new method of calculating non-road
emissions has been developed by the EPA called the NONROAD model. The NONROAD
model will be used to update the attainment modeling (1993 base case and
2007 future case) for the Houston area because the model has the best available
science with regard to emission factors and treatment of activity (equipment
usage rates) data. The NONROAD model works more like the highway emissions
model, MOBILE, in that temperatures and fuel qualities can be modified to
better reflect local conditions. The main change to the NONROAD model input
stream was the use of new equipment populations for diesel construction and
industrial equipment. Based on the study's findings, input files were generated
for use in EPA's NONROAD emissions model in order to estimate total pollution
levels from construction sources operating in the area. These results serve
as an update to the commission's previous estimates based on EPA's default
methodology. Even though the revised inventory has greatly reduced the uncertainty
in equipment emissions, the commission continually seeks to improve its inventories.
TSDA commented that they disagree with a statement in the proposal preamble
contending that small engines are the largest unregulated producer of hydrocarbons
in the state under the non-road mobile source category. EPA regulations, in
cooperation with CARB has already set new emission standards for January 1,
2001 that will cut hydrocarbon emissions by 59% by 2007. Briggs and Stratton
has cut emissions from their products by 70% since 1990.
The commission acknowledges that these sources are subject to the EPA emission
standards, however, lawn and garden equipment accounts for approximately 41
tpd of VOC. Small engines are the largest VOC emitters in the non-road category.
Lawn and garden equipment accounts for 37% of the 2007 HGA eight-county area
non-road VOC total, and recreational boating accounts for an additional 23%
on weekdays, (on weekends their share is much higher). The other 40% is spread
among many categories. The 41.2 tpd of VOCs from lawn and garden equipment
account for approximately 6.5% of the total anthropogenic eight-county VOCs.
Poulan and one individual commented that this equipment (two-stroke engines)
produces very little NO
x
.
Generally, two-stroke engines have low compression ratios, and valve timing
that leads to relatively low combustion temperatures and pressures. This means
that very little nitrogen (N
2
) is broken down
to allow NO
x
formation. This is also why two-
stroke engines tend to emit much higher amounts of VOCs from unburnt fuel.
These engines are a contributor to ozone formation and thus the commission
believes it is appropriate to include them in the adopted rule.
Friendly Robotics commented that they would like this rule to be amended
to contain a section which would encourage demonstration projects in the HGA
to educate the public and the dealer/retailer community about the alternative
use of robotic, electric, or battery-powered mowers in the four years before
this rule is implemented.
This rule has not been changed to incorporate these requests; however,
the commission supports the development of projects that will provide information
about the use of alternative types of equipment. The adopted rule allows commercial
operators to submit emission reduction plans that must demonstrate NO
STATUTORY AUTHORITY
The new sections are adopted under the TWC, §5.103, which authorizes
the commission to adopt rules necessary to carry out its powers and duties
under the TWC, and under the Texas Health and Safety Code, TCAA, §382.017,
which provides the commission the authority to adopt rules consistent with
the policy and purposes of the TCAA. The new sections are also adopted under
TCAA, §382.011, which authorizes the commission to control the quality
of the state's air; §382.012, which authorizes the commission to prepare
and develop a general, comprehensive plan for the control of the state's air; §382.019,
which authorizes the commission to adopt rules to control and reduce emissions
from engines used to propel land vehicles; and §382.039, which authorizes
the commission to develop and implement programs and other measures necessary
to demonstrate attainment and protect the public from exposure to hazardous
air contaminants from motor vehicles.
§114.452.Control Requirements.
(a)
No handheld or non-handheld, lawn and garden service equipment
powered by spark-ignition engines of 25 horsepower (hp) and below shall be
started or operated between the hours of 6:00 a.m. and noon, during the time
period from April 1 to October 31, in the counties listed in §114.459
of this title (relating to Affected Counties and Compliance Dates), except
as specified in subsections (b) and (c) of this section.
(b)
The following uses of lawn and garden service equipment
powered by spark-ignition engines of 25 hp and below are exempt from the requirements
of this division:
(1)
any use at a domestic residence by the owner of, or a resident
at, that domestic residence;
(2)
any use by a non-commercial operator; or
(3)
any use that is exclusively for emergency operations to
protect human health and safety or the environment, including equipment being
used in the repair of facilities, devices, systems, or infrastructure that
have failed, or are in danger of failing, in order to prevent immediate harm
to public health, safety, or the environment.
(c)
Commercial operators or persons not exempt under subsection
(b) of this section who submit an emissions reduction plan by May 31, 2003,
(which is approved by the executive director and the EPA no later than May
31, 2004) are exempt from operating hour restrictions upon implementation
of these rules in 2005, and are permitted to operate during the restricted
hours. The executive director may allow plans to be submitted after May 31,
2003. In any event, a plan must be approved prior to the use of that plan
for compliance with the requirements of this division. In order to be approved,
the plan must demonstrate nitrogen oxide and volatile organic compound reductions
equivalent to those required by the rules being requested for exemption, and
must contain adequate enforcement provisions.
(d)
Commercial operator is defined as any person who receives
payment or compensation in exchange for operating lawn and garden service
equipment powered by spark-ignition engines of 25 hp or below where the payment
or compensation is required to be reported as income by the United States
Internal Revenue Code. This term also includes any employees or contractors
of any person as defined in the Texas Clean Air Act, §382.003(10).
§114.459.Affected Counties and Compliance Dates.
Effective April 1, 2005, persons in the following counties shall be
in compliance with §114.452 of this title (relating to Control Requirements).
These include Brazoria, Fort Bend, Galveston, Harris, and Montgomery Counties
in the Houston/Galveston ozone nonattainment area.
This agency hereby certifies that the adoption has been reviewed
by legal counsel and found to be a valid exercise of the agency's legal authority.
Filed with the Office of
the Secretary of State on December 29, 2000.
TRD-200009096
Margaret Hoffman
Director. Environmental Law Division
Texas Natural Resource Conservation Commission
Effective date: January 18, 2001
Proposal publication date: August 25, 2000
For further information, please call: (512) 239-0348
30 TAC §§114.470, 114.472, 114.476, 114.477, 114.479
The Texas Natural Resource Conservation Commission (commission)
adopts new §114.470, Definitions; §114.472, Control Requirements; §114.476,
Reporting and Recordkeeping Requirements; §114.477, Exemptions; and §114.479,
Affected Counties. The commission adopts these new sections in new Division
8, Houston/Galveston Heavy Equipment Fleets - Compression-Ignition Engines;
Subchapter I, Non-road Engines; Chapter 114, Control of Air Pollution from
Motor Vehicles, and revisions to the state implementation plan (SIP) in order
to reduce ambient concentrations of ground-level ozone in the Houston/Galveston
(HGA) ozone nonattainment area through the accelerated purchase of United
States Environmental Protection Agency (EPA) certified Tier 2 and Tier 3 non-road
equipment 50 horsepower (hp) and larger. These new sections are one element
of the control strategy for the HGA Post-1999 Rate-of-Progress (ROP)/Attainment
Demonstration SIP. Section 114.477 is adopted
with
changes
to the proposed text as published in the August 25, 2000 issue
of the
Texas Register
(25 TexReg 8230). Sections
114.470, 114.472, 114.476, and 114.479 are adopted
without changes
to the proposed text and will not be republished.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE ADOPTED RULES
The HGA ozone nonattainment area is classified as Severe-17 under the Federal
Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401
et seq.), and therefore is required to attain the one-hour ozone standard
of 0.12 parts per million (ppm) by November 15, 2007. In addition, 42 USC, §7502(a)(2),
requires attainment as expeditiously as practicable, and 42 USC, §7511a(d),
requires states to submit ozone attainment demonstration SIPs for severe ozone
nonattainment areas such as HGA. The HGA area, defined by Brazoria, Chambers,
Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has
been working to develop a demonstration of attainment in accordance with 42
USC, §7410. On January 4, 1995, the state submitted the first of its
Post-1996 SIP revisions for HGA.
The January 1995 SIP consisted of urban airshed model (UAM) modeling for
1988 and 1990 base-case episodes, adopted rules to achieve a 9% ROP reduction
in volatile organic compounds (VOC), and a commitment schedule for the remaining
ROP and attainment demonstration elements. At the same time, but in a separate
action, the State of Texas filed for the temporary nitrogen oxides (NO
Around the same time as the 1995 submittal, EPA policy regarding SIP elements
and timelines went through changes. Two national programs in particular resulted
in changing deadlines and requirements. The first of these programs was the
Ozone Transport Assessment Group (OTAG). This group grew out of a March 2,
1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and
Radiation, that allowed states to postpone completion of their attainment
demonstrations until an assessment of the role of transported ozone and precursors
had been completed for the eastern half of the nation, including the eastern
portion of Texas. Texas participated in this study, and it has been concluded
that Texas does not significantly contribute to ozone exceedances in the Northeastern
United States. The other major national initiative that has impacted the SIP
planning process is the revision to the national ambient air quality standard
(NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing
the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996,
concurrent with the proposal of the standards, the EPA proposed an interim
implementation plan (IIP) that it believed would help areas like HGA transition
from the old to the new standard. In an attempt to avoid a significant delay
in planning activities, Texas began to follow this guidance, and readjusted
its modeling and SIP development timelines accordingly. When the new standard
was published, the EPA decided not to publish the IIP, and instead stated
that, for areas currently exceeding the one-hour ozone standard, that standard
would continue to apply until it is attained. The FCAA requires that HGA attain
the standard by November 15, 2007.
The EPA issued revised draft guidance for areas such as HGA that do not
attain the one-hour ozone standard. The commission adopted on May 6, 1998
and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained
the following elements in response to the EPA guidance: UAM modeling based
on emissions projected from a 1993 baseline out to the 2007 attainment date;
an estimate of the level of VOC and NO
x
reductions
necessary to achieve the one-hour ozone standard by 2007; a list of control
strategies that the state could implement to attain the one-hour ozone standard;
a schedule for completing the other required elements of the attainment demonstration;
a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the
EPA believed made the previous version of that SIP unapprovable; and evidence
that all measures and regulations required by Subpart 2 of Title I of the
FCAA to control ozone and its precursors have been adopted and implemented,
or are on an expeditious schedule to be adopted and implemented.
In November 1998, the SIP revision submitted to the EPA in May 1998 became
complete by operation of law. However, the EPA stated that it could not approve
the SIP until specific control strategies were modeled in the attainment demonstration.
The EPA specified a submittal date of November 15, 1999 for this modeling.
In a letter to the EPA dated January 5, 1999, the state committed to model
two strategies showing attainment.
As the HGA modeling protocol evolved, the state eventually selected and
modeled seven basic modeling scenarios. As part of this process, a group of
HGA stakeholders worked closely with commission staff to identify local control
strategies for the modeling. Some of the scenarios for which the stakeholders
requested evaluation included options such as California-type fuel and vehicle
programs, as well as an acceleration simulation mode equivalent motor vehicle
inspection and maintenance program. Other scenarios incorporated the estimated
reductions in emissions that were expected to be achieved throughout the modeling
domain as a result of the implementation of several voluntary and mandatory
state-wide programs adopted or planned independently of the SIP. It should
be made clear that the commission did not propose that any of these strategies
be included in the ultimate control strategy submitted to the EPA in 2000.
The need for and effectiveness of any controls which may be implemented outside
the HGA eight-county area will be evaluated on a county-by-county basis.
The SIP revision was adopted by the commission on October 27, 1999, submitted
to the EPA by November 15, 1999, and contained the following elements: photochemical
modeling of potential specific control strategies for attainment of the one-hour
ozone standard in the HGA area by the attainment date of November 15, 2007;
an analysis of seven specific modeling scenarios reflecting various combinations
of federal, state, and local controls in HGA (additional scenarios H1 and
H2 build upon Scenario VIf); identification of the level of reductions of
VOC and NO
x
necessary to attain the one-hour
ozone standard by 2007; a 2007 mobile source budget for transportation conformity;
identification of specific source categories which, if controlled, could result
in sufficient VOC and/or NO
x
reductions to attain
the standard; a schedule committing to submit by April 2000 an enforceable
commitment to conduct a mid-course review; and a schedule committing to submit
modeling and adopted rules in support of the attainment demonstration by December
2000.
The April 19, 2000 SIP revision for HGA contained the following enforceable
commitments by the state: to quantify the shortfall of NO
x
reductions needed for attainment; to list and quantify potential
control measures to meet the shortfall of NO
x
reductions needed for attainment; to adopt the majority of the necessary rules
for the HGA attainment demonstration by December 31, 2000, and to adopt the
rest of the shortfall rules as expeditiously as practical, but no later than
July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform
a mid- course review by May 1, 2004; and to perform modeling of mobile source
emissions using the EPA mobile source emissions model (MOBILE6), to revise
the on-road mobile source budget as needed, and to submit the revised budget
within 24 months of the model's release. In addition, if a conformity analysis
is to be performed between 12 months and 24 months after the MOBILE6 release,
the state will revise the motor vehicle emissions budget (MVEB) so that the
conformity analysis and the SIP MVEB are calculated on the same basis.
In order for the state to have an approvable attainment demonstration,
the EPA indicated that the state must adopt those strategies modeled in the
November submittal and then adopt sufficient controls to close the remaining
gap in NO
x
emissions. The modeling and other
analysis supporting these rules and the HGA SIP indicate a gap of approximately
an additional 91 tons per day (tpd) of NO
x
reductions
is necessary for an approvable attainment demonstration. The commission estimates
that this measure will achieve a minimum of 12.2 tpd of NO
x
reductions and is therefore a necessary measure to consider for closing
the gap and successfully demonstrating attainment.
The emission reduction requirements included as part of this SIP revision
represent substantial, intensive efforts on the part of stakeholder coalitions
in the HGA area. These coalitions, involving local governmental entities,
elected officials, environmental groups, industry, consultants, and the public,
as well as the commission and the EPA, have worked diligently to identify
and quantify potential control strategy measures for the HGA attainment demonstration.
Local officials from the HGA area have formally submitted a resolution to
the commission, requesting the inclusion of many specific emission reduction
strategies.
This rule adoption is one element of the control strategy for the HGA SIP.
Adoption and implementation of this control strategy is necessary in order
for the HGA nonattainment area to comply with the requirements of the FCAA
and achieve attainment for ozone. Additional elements of the control strategy
for the HGA SIP are being adopted concurrently in this issue of the
The amount of NO
x
reductions required for
the area to attain the ozone NAAQS has been estimated by extensive use of
sophisticated air quality grid modeling, which because of its scientific and
statutory grounding, is the chief policy tool for designing emission reduction
strategies. The FCAA, 42 USC, §7511a(c)(2), requires the use of photochemical
grid modeling for ozone nonattainment areas designated serious, severe, or
extreme. The modeling has been conducted with input from a technical oversight
committee. Commission staff have continued to improve the air quality modeling
technology and refine emission inventory data. Numerous emission control strategies
were considered in developing the modeling. Varying degrees of reductions
from point sources, on- road and non-road mobile sources, and area sources
were analyzed in multiple iterations of modeling, to test the effectiveness
of different NO
x
reductions. The attainment demonstration
modeling and other analysis submitted for public hearing and comment concurrently
with the HGA SIP show that a significant amount of NO
x
reductions practicably achievable are necessary from ozone control
strategies in order for the HGA nonattainment area to achieve the ozone NAAQS
by 2007, including reductions from surrounding counties included in the HGA
consolidated metropolitan statistical area (CMSA).
Additionally, reductions associated from the ozone control strategies that
will be implemented outside the HGA nonattainment area will benefit the HGA
nonattainment area. This is due to the regional nature of air pollution, the
contribution from mobile sources, and the economies of scale and associated
market advantages related to distribution networks for some strategies. At
the time the 1990 FCAA Amendments were enacted, the focus on controlling ozone
pollution was centered on local controls. However, for many years an ever
increasing number of air quality professionals have concluded that ozone is
a regional problem requiring regional strategies in addition to local control
programs. As nonattainment areas across the United States prepared attainment
demonstration SIPs in response to the 1990 FCAA Amendments, several areas
found that modeling attainment was made much more difficult, if not impossible,
due to high ozone and ozone precursor levels entering from the boundaries
of their respective modeling domains, commonly called transport. Recent science
indicates that regional approaches may provide improved control of ozone air
pollution.
The current SIP revision contains rules, enforceable commitments, photochemical
modeling analyses and calculation of the remaining NO
x
reductions required to reach attainment (gap calculation) in support
of the HGA ozone attainment demonstration. In addition, this SIP contains
post-1999 ROP plans for the milestone years 2002 and 2005, and for the attainment
year 2007. The SIP also contains enforceable commitments to implement further
measures, if needed, in support of the HGA attainment demonstration, as well
as a commitment to perform and submit a mid-course review.
The HGA ozone nonattainment area will need to ultimately reduce NO
The commission adopts these amendments to Chapter 114 and revisions to
the SIP in order to control ground-level ozone in the HGA ozone nonattainment
area, and the adopted rules are one element of the control strategy for the
HGA Post-1999 ROP/Attainment Demonstration SIP. The purpose of these adopted
rules is to establish the accelerated purchase and operation of cleaner non-
road, compression-ignition fleet equipment within the HGA nonattainment area
which will reduce NO
x
and VOC emissions that
are necessary for the counties included in the HGA nonattainment area to be
able to demonstrate attainment with NAAQS.
The EPA has been regulating highway (on-road) cars and trucks since the
early 1970s and continues to set increasingly stringent emissions standards
for such vehicles. After making considerable progress in controlling the emissions
from on-road vehicles, the EPA turned its attention to non-road engines, which
also contribute significantly to air pollution.
Diesel engines, also referred to as compression-ignition engines, dominate
the large non-road engine market. Examples of non-road equipment that use
diesel engines include: agricultural equipment such as tractors, balers, and
combines; construction equipment such as backhoes, graders, and bulldozers;
general industrial equipment such as concrete/industrial saws, crushing equipment,
and scrubber/sweepers; lawn and garden equipment such as garden tractors,
rear engine mowers, and chipper/grinders; material handling equipment such
as heavy forklifts; and utility equipment such as generators, compressors,
and pumps.
The EPA adopted regulations in 40 Code of Federal Regulations Part 89 (40
CFR 89), Control of Emissions from New and In-use Nonroad Engines, as effective
June 17, 1994. Under 40 CFR 89, compression-ignition engines greater than
50 hp must comply with Tier 1 emissions standards that are being phased in
between calendar years 1996 and 2000, depending on the size of the engine.
Under the Tier 1 standards, the EPA projects that NO
x
emissions from new non-road, compression-ignition equipment will
be reduced by over 30% from uncontrolled levels of unregulated engines. The
Tier 1 standards do not apply to engines used in underground mining equipment,
locomotives, and marine vessels. The Mine Safety and Health Administration
is responsible for setting requirements for underground mining equipment.
Locomotives and marine vessels are covered by separate EPA programs.
On October 23, 1998, the EPA revised 40 CFR 89 and adopted more stringent
emission standards for NO
x
, hydrocarbons (HC,
which are also called VOC), and particulate matter (PM) for new non-road,
compression-ignition engines. Engines used in underground mining equipment,
locomotives, and marine vessels over 50 hp are not included. This comprehensive
new program phases in more stringent Tier 2 standards for all engine sizes
from the model years 2001 to 2006, and yet more stringent Tier 3 standards
from the model years 2006 to 2008. The following figure, which was extracted
from the Table 1-1 of the "Final Regulatory Impact Analysis: Control of Emissions
from Non-road Diesel Engines," (EPA 420-R-98-016, dated August 1998) shows
the emission standards adopted by EPA in 40 CFR, §89.112. Also, the new
program includes a voluntary program called the "Blue Sky Series" engine program
to encourage the production of advanced, very low-emitting engines. Under
these new standards, the EPA projects that emissions from new non-road, compression-ignition
equipment will be further reduced by 60% for NO
x
and 40% for PM compared to the emission levels of engines meeting the Tier
1 standards.
Figure 1: 30 TAC Chapter 114 - Preamble
As part of the attainment demonstration SIP for the Dallas/Fort Worth (DFW)
ozone nonattainment area, the commission adopted accelerated non-road, compression-ignition
fleet rules (§§114.410, 114.412, 114.416, 114.417, and 114.419).
The adopted new rules apply requirements identical to the existing DFW rules
in the eight-county HGA ozone nonattainment counties.
Non-road equipment covered by these rules only includes equipment that
is used exclusively for non-road purposes because the federal Tier2/Tier 3
standards only apply to non-road engines. In other words, the rules cover
non-road equipment that do not have a license plate and cannot be used on
roads. Dump trucks and other equipment that are used both on-road and off-road
are not subject to the requirements of these rules.
The adopted rules will require persons in the HGA nonattainment area which
own or operate certain non-road equipment powered by compression-ignition
engines 50 hp and up to meet the following requirements. For the portion of
the fleet that is 50 hp up to 100 hp, the owner or operator must ensure that
such equipment will consist of 100% Tier 2 non-road equipment by the end of
the calendar year 2007. For the portion of the fleet that is 100 hp up to
750 hp, the owner or operator must ensure that such equipment consist of a
minimum of 50% Tier 3 non-road equipment and the remainder Tier 2 non-road
equipment by the end of the calendar year 2007. Finally, for the portion of
the fleet that is greater than 750 hp, the owner or operator must ensure that
such equipment consist of 100% Tier 2 engines by the end of calendar year
2007. This will accelerate the turnover rate of compression-ignition, engine-powered,
non-road equipment that would occur as a result of the federal Tier 2/Tier
3 program. Alternatively, an affected person may be exempted from these requirements
if an emission reduction plan is developed that will achieve emissions reductions
equivalent to the full implementation of these rules. As part of this plan
an owner or operator may achieve these reductions, in whole or in part, by
obtaining emission reduction credits (ERC), mobile emission reduction credits
(MERC), discrete emission reduction credit (DERC), or mobile discrete emission
reduction credit (MDERC) in accordance with adopted new §114.477 and
30 TAC Chapter 101, General Air Rules, §101.29, Emission Credit Banking
and Trading. In concurrent rulemaking (rule log number 1998-089-101-AI), the
emission credit banking and trading rules are being moved to Chapter 101,
Subchapter H, Emissions Banking and Trading, Division 1, Emission Credit Banking
and Trading and Division 4, Discrete Emission Credit Banking and Trading.
The HGA area needs emissions reductions earlier than what the natural turnover
would allow; therefore, these adopted rules will require that Tier 2 and Tier
3 equipment be purchased at an accelerated rate once they become available
under the EPA schedule outlined in 40 CFR 89. The adopted rules exempt non-road
engines used in locomotives, underground mining equipment, marine application,
aircraft, airport ground support equipment (GSE), equipment used solely for
agricultural and/or logging purposes, emergency equipment, and freezing weather
equipment.
The rules will affect non-road diesel equipment 50 hp and larger such as
construction, industrial, commercial, and lawn and garden equipment. Examples
of equipment used in construction applications include bore/drill rigs, cement
and mortar mixers, concrete/industrial saws, cranes, crawler tractors, crushing/processing
equipment, dumpers/tenders, excavators, graders, off-highway tractors, off-
highway trucks, pavers, paving equipment, plate compactors, rollers, rough
terrain forklifts, rubber- tire dozers, rubber-tire loaders, scrapers, signal
boards/light plants, skid-steer loaders, surfacing equipment, tampers/rammers,
tractors/loaders/backhoes, and trenchers. Examples of equipment used in industrial
applications include aerial lifts, forklifts, general industrial equipment,
material handling equipment, refrigeration/air conditioning units, scrubber/sweepers,
and terminal tractors. Examples of equipment used in lawn and garden applications
include chippers/stump grinders, commercial turf equipment, lawn and garden
tractors, and leafblowers/vacuums. Examples of equipment used in commercial
applications include air compressors, gas compressors, generator sets, pressure
washers, pumps, and welders.
The costs of meeting the new federal emission standards are expected to
add about 1.0% to the purchase price of typical new non-road, compression-ignition
equipment, although for some equipment the standards may cause price increases
on the order of 2.0% to 3.0%. However, the cost of this program is the cost
of having to replace the non-road, compression-ignition fleet on an accelerated
schedule, not the cost of Tier 2 and Tier 3 engines. The cost of Tier 2 and
Tier 3 engines is already accounted for in the EPA regulations, not as a result
of these rules. The program is expected to cost between $30 million to $42
million average annual cost.
The commission solicited comment on additional flexibilities relating to
rule content and implementation which have not been addressed in this or other
concurrent rulemakings. These flexibilities may be available for both mobile
and stationary sources. Additional flexibilities may also be achieved through
innovative and/or emerging technology which may become available in the future.
Additional sources of funds for incentive programs may become available to
substitute for some of the measures considered here. There were 19 comments
received regarding flexibilities which are addressed in the ANALYSIS OF TESTIMONY
section of this preamble.
SECTION-BY-SECTION DISCUSSION
Rules regarding an accelerated purchase of federal Tier 2 and Tier 3 non-road
diesel equipment were adopted for the DFW ozone nonattainment area on April
19, 2000. These rules were adopted in Chapter 114, Subchapter I, Division
2, §114.410, Definitions; §114.412, Control Requirements; §114.416,
Reporting and Recordkeeping Requirements; §114.417, Exemptions; and §114.419,
Affected Counties. This rulemaking action adopts identical requirements which
apply to the eight-county HGA ozone nonattainment area.
The adopted new §114.470 adds definitions for Blue Sky Series engine,
compression- ignition engine, fleet, non-road engine, non-road equipment,
Tier 2 engine, and Tier 3 engine.
The adopted new §114.472 requires persons in the affected counties
listed in §114.479, which own or operate non-road equipment powered by
compression-ignition engines to use non-road equipment powered by Tier 2 and
Tier 3 compression engines. The phase-in schedule specified in these rules
accelerates the natural turnover of non-road equipment. To ensure the equipment
is available, the phase-in schedule specified in these rules is set up so
that compliance dates come after the implementation dates of the new federal
standard as specified in the federal rules in 40 CFR §89.112, as amended
on October 23, 1998. For the portion of the non-road fleets powered by compression-ignition
engines greater than or equal to 100 hp, but less than or equal to 750 hp,
the rule requires a gradually increased percentage of Tier 2 and Tier 3 equipment
required, so that by the end of calendar year 2007, at least 50% of the affected
portion of the fleet shall meet Tier 3 standards and the remainder of the
affected fleet shall meet Tier 2 standards. For the portion of the fleet greater
than or equal to 50 hp, but less than 100 hp, the adopted rule requires that
100% of the equipment meet Tier 2 standards by the end of calendar year 2007.
For engines greater than 750 hp, the adopted rule requires that 100% of the
affected fleet be Tier 2 engines by the end of calendar year 2007. The rule
also allows the non-road engines designated as "Blue Sky Series" engines to
be counted toward the percentage requirements as either Tier 2 or Tier 3 engines.
The "Blue Sky Series" engine program is a voluntary EPA program that allows
for earlier introduction of cleaner engines. The emission standards for the
Blue Sky Series program are the same as Tier 3 emission standards. Finally,
the adopted rule will allow an EPA-certified retrofit of newly purchased engines,
in order to meet the Tier 2 or Tier 3 emission standards, be allowed to meet
the percentage requirements. This retrofit allowance is adopted because some
newly purchased engines may be able to meet the Tier 2 and Tier 3 emission
standards by being retrofitted. Therefore, for an affected entity to meet
the percentage requirements, they may purchase new equipment or retrofit existing
engines if there is an EPA-certified retrofit available.
The adopted new §114.476 requires persons subject to §114.472
to submit annual fleet reports. The adopted rule also requires them to maintain
copies of the submitted reports for a minimum of three years.
The adopted new §114.477 exempts locomotives, underground mining equipment,
marine engines, aircraft engines, airport GSE, and agricultural equipment.
Locomotives, underground mining equipment, marine engines, and aircraft engines
are exempt from these adopted rules because they are not regulated by the
EPA non-road rule. Airport GSE is exempt from these rules because it is being
regulated by another strategy being adopted concurrently. The exemption for
airport GSE is intended to cover all equipment that is used to service aircraft
during passenger and/or cargo loading and unloading, maintenance, and other
ground-based operations. Exemptions from this equipment category which may
exist in other rules or agreements, such as freezing weather equipment or
leased equipment, do not apply here. Agricultural equipment is exempt from
the adopted rules because of its small contribution (less than 1.0%) to non-road
emissions, and because it is operated primarily in rural areas. Also, the
commission adopts an exemption for equipment used exclusively for emergency
operations and for equipment used exclusively for freezing weather operations
due to their low impact on air quality during the ozone season. In response
to comments received the commission clarified the language to make clear that
logging uses are exempt.
In the rulemaking for the DFW area construction equipment operating restrictions
rules, the commission specifically requested comment on allowing the use of
added controls such as catalytic converters or other after-market devices,
or the use of EPA-certified cleaner equipment, to exempt such equipment from
the operating restrictions of these rules. In response to the DFW exemption
comments and other comments to those rules concerning the difficulty in complying
with these rules, the commission adopts §114.477(b). This subsection
allows owners or operators to be exempt from the requirements of these rules
if they submit an emissions reduction plan by May 31, 2002, that is approved
by the executive director and the EPA by May 31, 2003. The executive director
may allow plans to be submitted after May 31, 2002. In any event, a plan must
be approved prior to the use of that plan for compliance with the requirements
of this division. The commission anticipates that by offering this exemption,
the entities affected by these rules, the trade associations representing
these entities, and the manufacturers will be encouraged to accelerate the
research and development of emissions-reducing technology for equipment that
will enable affected entities to meet the exemption. Each plan must describe
in detail how the owner or operator will modify the equipment fleet to reduce
NO
x
emissions by June 1, 2005 by a target amount
equivalent to the total reductions achieved by implementation of these rules.
If equipment subject to these rules is also subject to the HGA construction
equipment operating restrictions rules, and the owner or operator would like
to be exempt from both sets of rules, then the plan must reduce NO
x
emissions by a target amount equivalent to the total reductions achieved
by both sets of rules. If the plan demonstrates that these reductions will
occur by June 1, 2005, the reductions will be considered equivalent for purposes
of timing. The commission will apply emissions inventory factors for equipment
used in the modeling to develop these rules to quantify the emissions reductions
resulting from the fleet modifications. The commission will develop a guidance
document to assist operators in developing their plans. The guidance document
will contain both the target emissions amount operators must meet, as well
as emission factors for each type of equipment affected by the rules, and
will offer guidance on how to calculate total emissions reductions for an
equipment fleet. The commission made changes to the language in this subsection
(b) to clarify and make the language consistent with that in the HGA construction
equipment operating restrictions rules, §114.487 of this title (relating
to Exemptions).
The commission is requiring submission of the emission reduction plans
by May 31, 2002 to allow sufficient time to review and quantify the collective
emissions reductions the plans propose. The commission will complete the reviews
by May 31, 2003, which coincides with the planned mid-course review of all
control measures included in the SIP. After reviewing the plans, the commission
will determine whether the collective emissions reductions adopted by the
plans are equivalent to the reductions achieved from implementing both these
rules.
The adopted new §114.479 specifies the counties that are subject to
the new requirements. The counties included in the eight-county HGA nonattainment
area are Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery,
and Waller.
FINAL REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the rulemaking action in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225, and has determined
that the rulemaking meets the definition of a "major environmental rule" as
defined in that statute. "Major environmental rule" means a rule of which
the specific intent is to protect the environment or reduce risks to human
health from environmental exposure and that may adversely affect in a material
way the economy, a sector of the economy, productivity, competition, jobs,
the environment, or the public health and safety of the state or a sector
of the state.
These adopted rules do not meet any of the four applicability criteria
for requiring a regulatory analysis of "major environmental rule" as defined
in the Texas Government Code. Section 2001.0225 applies only to a major environmental
rule the result of which is to: 1) exceed a standard set by federal law, unless
the rule is specifically required by state law; 2) exceed an express requirement
of state law, unless the rule is specifically required by federal law; 3)
exceed a requirement of a delegation agreement or contract between the state
and an agency or representative of the federal government to implement a state
and federal program; or 4) adopt a rule solely under the general powers of
the agency instead of under a specific state law.
As discussed earlier in this preamble, this rule adoption is one element
of the control strategy for the HGA SIP. Adoption and implementation of this
control strategy is necessary in order for the HGA nonattainment area to comply
with the requirements of the FCAA and achieve attainment for ozone. Additional
elements of the control strategy for the HGA SIP are being adopted concurrently
in this issue of the
Texas Register
, or were
included in the HGA SIP considered by the commission on December 6, 2000,
and planned to be submitted to EPA by December 31, 2000.
The rules are intended to protect the environment or reduce risks to human
health from environmental exposure to ozone and will affect in a material
way, the economy, a sector of the economy, productivity, competition, jobs,
the environment, or the public health and safety of the state or a sector
of the state. The rules would require units of state and local government,
businesses, and persons in the eight-county HGA ozone nonattainment area which
own or operate non-road equipment powered by compression-ignition equipment
to meet the following requirements. For the portion of the fleet that is 50
hp up to 100 hp, owners and operators must ensure that such equipment will
consist of 100% Tier 2 non-road equipment by the end of the calendar year
2007. For the portion of the fleet that is 100 hp up to 750 hp, owners and
operators must ensure that such equipment consist of a minimum of 50% Tier
3 non-road equipment and the remainder Tier 2 non-road equipment by the end
of the calendar year 2007. Finally, for the portion of the fleet that is greater
than 750 hp, owners and operators must ensure that such equipment consist
of 100% Tier 2 engines by the end of calendar year 2007.
This air pollution control program is part of the strategy to reduce NO
These rules do not exceed an express standard set by federal law, since
they implement requirements of the FCAA. Under 42 USC, §7410, states
are required to adopt a SIP which provides for "implementation, maintenance,
and enforcement" of the primary NAAQS in each air quality control region of
the state. These rules were specifically developed as part of an overall control
strategy to meet the ozone NAAQS set by the EPA under 42 USC, §7409.
While 42 USC, §7410 does not require specific programs, methods, or reductions
in order to meet the standard, state SIPs must include "enforceable emission
limitations and other control measures, means or techniques (including economic
incentives such as fees, marketable permits, and auctions of emissions rights),
as well as schedules and timetables for compliance as may be necessary or
appropriate to meet the applicable requirements of this chapter," (meaning
42 USC, Chapter 85, Air Pollution Prevention and Control). It is true that
the FCAA does require some specific measures for SIP purposes, like the inspection
and maintenance program, but those programs are the exception, not the rule,
in the SIP structure of the FCAA. The provisions of the FCAA recognize that
states are in the best position to determine what programs and controls are
necessary or appropriate in order to meet the NAAQS. This flexibility allows
states, affected industry, and the public, to collaborate on the best methods
for attaining the NAAQS for the specific regions in the state. Even though
the FCAA allows states to develop their own programs, this flexibility does
not relieve a state from developing a program that meets the requirements
of 42 USC, §7410. In order to avoid federal sanctions, states are not
free to ignore the requirements of 42 USC, §7410 and must develop programs
to assure that the nonattainment areas of the state will be brought into attainment
on schedule. Thus, while specific measures are not prescribed, both a plan
and emission reductions are required to assure that the nonattainment areas
of the state will be able to meet the attainment deadlines set by the FCAA.
The EPA has provided the criteria for both the submission and evaluation of
attainment demonstrations developed by states to comply with the FCAA. This
criteria requires states to provide, in addition to other information, photochemical
modeling and an analysis of specific emission reduction strategies necessary
to attain the NAAQS. The commission's photochemical modeling and other analysis
indicate that substantial emission reductions from both mobile and point source
categories are necessary in order to demonstrate attainment. In this case,
this rulemaking is intended to achieve emission reductions in the HGA nonattainment
area. Specifically, as noted elsewhere in this rule preamble, the emission
reductions associated with these rules are a necessary element of the attainment
demonstration required by the FCAA.
In addition, 42 USC, §7502(a)(2), requires attainment as expeditiously
as practicable, and 42 USC, §7511a(d), requires states to submit ozone
attainment demonstration SIPs for severe ozone nonattainment areas such as
HGA. By policy, the EPA requires photochemical grid modeling to demonstrate
whether the 42 USC, §7511a(f), NO
x
measures
would contribute to ozone attainment. The commission has performed photochemical
grid modeling which predicts that NO
x
emission
reductions, such as those required by these rules, will result in reductions
in ozone formation in the HGA ozone nonattainment area and help bring HGA
into compliance with the air quality standards established under federal law
as NAAQS for ozone. The 42 USC, §7511a(f), exemption from NO
x
measures for HGA expired on December 31, 1997. The expiration of
the exemption under 42 USC, §7511a(f), was based on the finding that
NO
x
reductions in HGA are necessary for attainment
of the ozone standard. Therefore, the adopted amendments are necessary components
of and consistent with the ozone attainment demonstration SIP for HGA, required
by 42 USC, §7410.
During the 75th Legislative Session, Senate Bill (SB) 633 amended the Texas
Government Code to require agencies to perform a regulatory impact analysis
(RIA) of certain rules. The intent of SB 633 was to require agencies to conduct
an RIA of extraordinary rules. With the understanding that this requirement
would seldom apply, the commission provided a cost estimate for SB 633 that
concluded "based on an assessment of rules adopted by the agency in the past,
it is not anticipated that the bill will have significant fiscal implications
for the agency due to its limited application." The commission also noted
that the number of rules that would require assessment under the provisions
of the bill was not large. This conclusion was based, in part, on the criteria
set forth in the bill that exempted proposed rules from the full analysis
unless the rule was a major environmental rule that exceeds a federal law.
As previously discussed, 42 USC does not require specific programs, methods,
or reductions in order to meet the NAAQS; thus, states must develop programs
for each nonattainment area to ensure that area will meet the attainment deadlines.
Because of the ongoing need to address nonattainment issues, the commission
routinely proposes and adopts SIP rules. The legislature is presumed to understand
this federal scheme. If each rule proposed for inclusion in the SIP was considered
to be a major environmental rule that exceeds federal law, then every SIP
rule would require the full RIA contemplated by SB 633. This conclusion is
inconsistent with the conclusions reached by the commission in its cost estimate
and by the Legislative Budget Board (LBB) in its fiscal notes. Because the
legislature is presumed to understand the fiscal impacts of the bills it passes,
and that presumption is based on information provided by state agencies and
the LBB, the commission believes that the intent of SB 633 was only to require
the full RIA for rules that are extraordinary in nature. While the SIP rules
will have a broad impact, that impact is no greater than is necessary or appropriate
to meet the requirements of the FCAA.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
It is presumed that "when an agency interpretation is in effect at the time
the legislature amends the laws without making substantial change in the statute,
the legislature is deemed to have accepted the agency's interpretation."
The commission's interpretation of the RIA requirements is also supported
by a change made to the Texas Administrative Procedure Act (APA) by the legislature
in 1999. In an attempt to limit the number of rule challenges based upon APA
requirements, the legislature clarified that state agencies are required to
meet these sections of the APA against the standard of "substantial compliance."
Texas Government Code, §2001.035. The legislature specifically identified
Texas Government Code, §2001.0225 as falling under this standard. The
commission has substantially complied with the requirements of §2001.0225.
Therefore, in addition to not exceeding an express standard set by federal
law, these rules do not exceed state requirements, and are not adopted solely
under the general powers of the agency because the provisions of the Texas
Clean Air Act (TCAA), §§382.011, 382.012, 382.017, 382.019, and
382.039 authorize the commission to implement a plan for the control of the
states air quality, including measures necessary to meet federal requirements.
The remaining applicability criteria, pertaining to exceeding a delegation
agreement or contract between the state and the federal government does Texas
Government Code, §2001.0225.
The commission solicited public comment on the draft regulatory impact
analysis and received six comments. These comments are addressed in the ANALYSIS
OF TESTIMONY section of this preamble.
TAKINGS IMPACT ASSESSMENT
The commission evaluated this rulemaking action and performed an analysis
of whether the rules are subject to Texas Government Code, Chapter 2007. The
following is a summary of that analysis. The specific purpose of the adopted
rulemaking action would require persons in the eight-county HGA nonattainment
area which own or operate non-road, compression-ignition equipment to meet
the following requirements. For the portion of the fleet that is 50 hp up
to 100 hp, the owner or operator must ensure that such equipment will consist
of 100% Tier 2 non-road equipment by the end of the calendar year 2007. For
the portion of the fleet that is 100 hp up to 750 hp, the owner or operator
must ensure that such equipment consist of a minimum of 50% Tier 3 non-road
equipment and the remainder Tier 2 non-road equipment by the end of the calendar
year 2007. Finally, for the portion of the fleet that is greater than 750
hp, the owner or operator must ensure that such equipment consist of 100%
Tier 2 engines by the end of calendar year 2007. This adopted rulemaking action
will act as an air pollution control strategy to reduce NO
x
emissions necessary for the eight counties included in the HGA ozone
nonattainment area to be able to demonstrate attainment with the ozone NAAQS.
Promulgation and enforcement of this rule will not burden private, real property.
Also, Texas Government Code, §2007.003(b)(13), states that Chapter 2007
does not apply to an action that: 1) is taken in response to a real and substantial
threat to public health and safety; 2) is designed to significantly advance
the health and safety purpose; and 3) does not impose a greater burden than
is necessary to achieve the health and safety purpose. Although the adopted
rules do not directly prevent a nuisance, or prevent an immediate threat to
life or property, they do prevent a real and substantial threat to public
health and safety, and partially fulfill a federal mandate under 42 USC, §7410.
In addition, §2007.003(b)(4) provides that Chapter 2007 does not apply
to these adopted rules since it is reasonably taken to fulfill an obligation
mandated by federal law. This action is taken in response to the HGA area
exceeding the NAAQS for ground-level ozone, which adversely affects public
health, primarily through irritation of the lungs. The action significantly
advances the health and safety purpose by reducing ambient NO
x
and ozone levels in HGA. Attainment of the ozone standard will eventually
require substantial NO
x
reductions. Any NO
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that the adopted rulemaking relates to an action
or actions subject to the Texas Coastal Management Program (CMP) in accordance
with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources
Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter
281, Subchapter B, concerning Consistency with the CMP. As required by 30
TAC §281.45(a)(3) and 31 TAC §505.11(b)(2), relating to actions
and rules subject to the CMP, commission rules governing air pollutant emissions
must be consistent with the applicable goals and policies of the CMP. The
commission reviewed this action for consistency with the CMP goals and policies
in accordance with the rules of the Coastal Coordination Council, and determined
that the action is consistent with the applicable CMP goals and policies.
The CMP goal applicable to this rulemaking action is the goal to protect,
preserve, and enhance the diversity, quality, quantity, functions, and values
of coastal natural resource areas (31 TAC §501.12(1)). No new sources
of air contaminants will be authorized and NO
x
air emissions will be reduced as a result of these rules. The CMP policy applicable
to this rulemaking action is the policy that commission rules comply with
regulations in 40 CFR, to protect and enhance air quality in the coastal area
(31 TAC §501.14(q)). This rulemaking action complies with 40 CFR 50,
National Primary and Secondary Ambient Air Quality Standards, and 40 CFR 51,
Requirements for Preparation, Adoption, and Submittal Of Implementation Plans.
Therefore, in compliance with 31 TAC §505.22(e), this rulemaking action
is consistent with CMP goals and policies.
The commission solicited comments on the consistency of the proposed rules
with the CMP during the public comment period and received no comments.
HEARINGS AND COMMENTERS
The commission held public hearings on this proposal at the following locations:
September 18, 2000, in Conroe and Lake Jackson; September 19, 2000 in Houston
(two hearings); September 20, 2000, in Katy and Pasadena; September 21, 2000,
in Beaumont, Amarillo, and Texas City; September 22, 2000, in Dayton, El Paso,
and Arlington; and September 25, 2000, in Austin and Corpus Christi. The comment
period closed at 5:00 p.m. on September 25, 2000. The following entities and
40 individuals provided oral testimony and/or submitted written testimony:
American Road & Transportation Builders Association (ARTBA); Associated
Builders & Contractors of Greater Houston (ABC); Associated General Contractors
of America, Houston Chapter (AGC-Houston); Associated General Contractors
of Texas (AGC-Texas); Baker Botts; Lloyd, Gosselink, Blevins, Rochelle, Baldwin &
Townsend, P.C. on behalf of BFI Waste Systems of North America, Inc. (BFI);
Brazoria County Criminal District Attorney Jeri Yenne on behalf of Brazoria
County Commissioners Court (Brazoria County); Brett & Wolff LLC (Brett &
Wolff); British Petroleum-Amoco (BP); Business Coalition for Clean Air (BCCA);
Chambers County Judge Jimmy Sylvia (Chambers County); City of Lake Jackson
(Lake Jackson); City of Missouri City (Missouri City); City of Simonton (Simonton);
City of Spring Valley (Spring Valley); Dow Chemical Company (Dow); Neal Gerber &
Eisenberg on behalf of Engine Manufacturers Association (EMA); Environmental
Defense (ED); ExxonMobil Corporation (ExxonMobil); Galveston-Houston Association
for Smog Prevention (GHASP); Harris County Judge Robert Eckels (Harris County);
Hispanic Community for Texas Citizens for a Solid Economy (TCSE-HC); Benthul &
Kean on behalf of Houston Construction Industry Coalition (HCIC); Houston
Metropolitan Planning Organization's Transportation Policy Council (Houston
MPO); League of Women Voters of the Houston area (LWV-Houston); League of
Women Voters of Texas (LWV- TX); Liberty County Sheriff Gregg Arthur (Liberty
County-Sheriff); RMT, Inc. on behalf of Montgomery County (Montgomery Co.);
Mothers for Clean Air (MCA); National Aeronautics and Space Administration
(NASA); Pamela Berger on behalf of Lee Brown, Mayor of Houston (Mayor of Houston);
Phillips 66 Company (Phillips 66); Port of Houston Authority (PHA); Public
Citizen; Reliant Energy, Inc. (REI); SEED Coalition (SEED); Sierra Club Houston
Regional Group (Sierra-Houston); Texas City Mayor Carlos Garza (Texas City);
Texas Department of Transportation (TxDOT); Texas Forestry Association (TFA);
Texas Logging Council (TLC); EPA; and Waste Management (WM). The following
entities and 11 individuals generally supported the proposal: BP, GHASP, Lake
Jackson, LWV-Houston, LWV-TX, Missouri City, Public Citizen, and SEED. The
following entities and 16 individuals generally opposed the proposal: ABC,
AGC-Texas, ARTBA, Baker Botts, BCCA, BFI, Brazoria County, Chambers County,
Dow, EMA, ExxonMobil, Harris County, HCIC, TCSE- HC, AGC-Houston, Liberty
County-Sheriff, Montgomery Co., PHA, Phillips 66, REI, Simonton, Spring Valley,
TFA, TLC, and WM. The following entities and 13 individuals suggested changes
to the proposal as stated in the ANALYSIS OF TESTIMONY section of this preamble:
ABC, AGC- Texas, ARTBA, BCCA, Baker Botts, BFI, Brett & Wolff, Chambers
County, Mayor of Houston, Dow, ED, EMA, EPA, ExxonMobil, Harris County, HCIC,
AGC-Houston, Sierra-Houston, Lake Jackson, Liberty County-Sheriff, MCA, Missouri
City, Montgomery Co., NASA, PHA, Simonton, Spring Valley, Texas City, TFA,
TLC, Houston MPO, TxDOT, and WM.
Phillips 66, REI, Dow, ExxonMobil, and one individual supported the comments
submitted by BCCA; therefore references to BCCA should be read to include
these commenters. The Mayor of Houston supported the comments submitted by
Harris County; therefore references to Harris County should be read to include
the Mayor of Houston. Harris County supported the comments submitted by the
Houston MPO; therefore references to the Houston MPO should be read to include
Harris County and the Mayor of Houston. Public Citizen supported the comments
submitted by ED; therefore references to ED should be read to include Public
Citizen.
ANALYSIS OF TESTIMONY
Legal Issues
AGC-Texas, ARTBA, BCCA, BFI, ExxonMobil, PHA, Phillips 66, and WM commented
on the draft RIA and stated that the proposed rules were not evaluated in
accordance with the analysis requirements for a major environmental rule.
The commenters stated that Texas Government Code, §2001.0225, requires
an RIA for certain major environmental rules. The commenters stated that the
commission must consider the benefits and costs of the proposed rules in relationship
to state agencies, local governments, the public, the regulated community,
and the environment. The commenters stated further that the commission must
also incorporate aspects of this analysis into the fiscal note in the proposed
rules, e.g., identify the costs and the benefits; describe reasonable alternative
methods for achieving the purpose of the rules considered by the agency; provide
the reasons for rejecting those alternatives; and identify the data and methodology
used in performing the analysis. The commenters stated that under §2001.0225(d)
the commission must also find that "compared to the alternative proposals
considered and rejected, the rule will result in the best combination of effectiveness
in obtaining the desired results and of economic costs not materially greater
than the costs of any alternative regulatory method considered."
The commenters stated that the rule proposal preamble statement, that the
rules are exempt from the RIA requirement because federal law mandates the
rules, is a legally flawed effort to avoid an RIA and may render the rules
invalid. The commenters stated that federal law does not mandate the control
requirements, emission rates, and use restrictions contained in the proposal
and asserted that many of the proposed rules exceed specific federal rules
and standards applicable to the same sources.
BFI commented that the commission failed to comply with its statutory obligations
to prepare a complete and accurate fiscal note and perform a meaningful RIA.
AGC-Texas and ExxonMobil commented that these rules exceed a standard set
by federal law, exceeds an expressed requirement of state law, and are adopted
solely under the general powers of the agency. ExxonMobil commented further
that the commission must incorporate aspects of this analysis into the fiscal
note and that such analysis should at least include: 1) identification of
the costs and the benefits; 2) reasonable alternative methods for achieving
the purpose of the rule considered; 3) reasoning for rejecting those alternatives;
and 4) identification of the data and methodology used in performing the analysis.
ExxonMobil commented that the commission must find that these rules will result
in the ". . . best combination of effectiveness in obtaining the desired results
and economic costs not materially greater than the costs of any alternative
regulatory method considered." AGC-Texas expanded on this in that they state
that the proposed rules will not result in the "best combination of effectiveness
in obtaining the desired result and economic costs not materially greater
than the costs of any alternative regulatory method considered." They commented
that many of the non-road control measures being considered as alternatives
are projected to cost between $3,000 and $15,000 per ton of NO
x
reduced. Furthermore, ARTBA, ExxonMobil, and WM commented that they
do not agree with the commission claim that these rules were exempt from these
requirements because federal law "specifically required" them. WM commented
that an RIA must be performed and offered for public comment before a proposal
can be finally adopted.
The commenters stated that the rule proposal preamble acknowledges that
the rule proposal components are "major environmental rules," but that the
commission asserted that an RIA is "seldom" required and is only required
for "extraordinary" rules. The commenters stated that these criteria appear
nowhere in the RIA requirements. The commenters stated that the rule proposal
preamble states that "while the SIP rules will have a broad impact, that impact
is no greater than is necessary or appropriate to meet the requirements of
the FCAA." The commenters stated that this "no greater than is necessary or
appropriate" determination is the conclusion that an RIA is designed to evaluate
and to offer for public review and comment. The commenters stated that the
rule proposal is well beyond any federal mandates for the covered sources
and are "extraordinary."
The commission agrees that these rules meet the definition of a major environmental
rule; however, the commission disagrees that its interpretation of the exemption
for federally mandated standards is legally flawed. While the rules may require
significant capital investment by equipment owners and operators, that alone
is not enough to trigger the RIA requirements. The Texas Government Code, §2001.0225,
only applies to a major environmental rule adopted by a state agency, the
result of which is to: 1) exceed a standard set by federal law, unless the
rule is specifically required by state law; 2) exceed an express requirement
of state law, unless the rule is specifically required by federal law; 3)
exceed a requirement of a delegation agreement or contract between the state
and an agency or representative of the federal government to implement a state
and federal program; or 4) adopt a rule solely under the general powers of
the agency instead of under a specific state law.
This rulemaking action does not meet any of these four applicability requirements,
and is adopted in substantial compliance with the RIA requirements in Texas
Government Code, §2001.035. These rules do not exceed an express standard
set by federal law, because the fleet requirements are specifically developed
to meet the ozone NAAQS set by the EPA under 42 USC, §7409. Title 42
USC, §7410 requires states to adopt a SIP which provides for "implementation,
maintenance, and enforcement" of the primary NAAQS in each air quality control
region of the state. While 42 USC, §7410 does not specifically prescribe
programs, methods, or reductions to meet the federal standard, state SIPs
must include "enforceable emission limitations and other control measures,
means or techniques (including economic incentives such as fees, marketable
permits, and auctions of emissions rights), as well as schedules and timetables
for compliance as may be necessary or appropriate to meet the applicable requirements
of this chapter" (meaning 42 USC, Chapter 85, Air Pollution Prevention and
Control). Title 42 USC does require some specific measures for SIP purposes,
such as an inspection and maintenance program, but those programs are the
exception, not the rule, in the federal SIP structure. The provisions of 42
USC recognize that states are in the best position to determine what programs
and controls are necessary or appropriate in order to meet the NAAQS. This
flexibility allows states, affected industry, and the public, to collaborate
on the best methods for attaining the NAAQS for the specific regions in the
state. In order to avoid federal sanctions, states are not free to ignore
the requirements of 42 USC, §7410, and must develop programs to assure
that the nonattainment areas of the state will be brought into attainment
on schedule. Failure to develop control strategies to demonstrate attainment
can result in federal sanctions. Thus, while specific measures are not prescribed,
both a plan and emission reductions are required to assure that the nonattainment
areas of the state will be able to meet the attainment deadlines set by 42
USC. The EPA has provided the criteria for both the submission and evaluation
of attainment demonstrations developed by states to comply with 42 USC. This
criteria requires states to provide, in addition to other information, photochemical
modeling and an analysis of specific emission reduction strategies necessary
to attain the NAAQS. The commission's photochemical modeling and other analysis
indicate that substantial emission reductions from both mobile and point source
categories are necessary in order to demonstrate attainment. In this case,
this rulemaking is intended to achieve reductions in ozone precursor emissions
in the HGA nonattainment area. Specifically, as noted elsewhere in this rule
preamble, the emission reductions associated with these rules are a necessary
element of the attainment demonstration required by 42 USC.
This conclusion is supported by the legislative history for Texas Government
Code, 2001.0225. During the 75th Legislative Session, SB 633 amended the Texas
Government Code to require agencies to perform a RIA of certain rules. The
intent of SB 633 was to require agencies to conduct an RIA of major environmental
rules that will have a material adverse impact, and will exceed a requirement
of state law, federal law, or a delegated federal program, or are adopted
solely under the general powers of the agency. The commission provided a cost
estimate for SB 633 that concluded "based on an assessment of rules adopted
by the agency in the past, it is not anticipated that the bill will have significant
fiscal implications for the agency due to its limited application." The commission
also noted that the number of rules that would require assessment under the
provisions of the bill was not large. Because of the ongoing need to address
nonattainment demonstrations required by federal law, the commission routinely
proposes and adopts SIP rules. If each rule proposed for inclusion in the
SIP was incorrectly considered as exceeding federal law, every SIP rule would
require the full RIA contemplated by SB 633. This result would be inconsistent
with the cost estimates and fiscal notes prepared by the commission and by
the LBB. Because the legislature is presumed to understand the fiscal impacts
of the bills it passes, and that presumption is based on information provided
by state agencies and the LBB, the commission believes that the intent of
SB 633 was only to require the full RIA for rules that meet the requirements
under §2001.0225(a). While the SIP rules will have a broad impact, that
impact is no greater than is necessary or appropriate to meet the requirements
of 42 USC. In other words, the proposed rules are intended to meet federal
and state law, and do not go above and beyond what is required to meet federal
or state statutes.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
It is presumed that "when an agency interpretation is in effect at the time
the legislature amends the laws without making substantial change in the statute,
the legislature is deemed to have accepted the agency's interpretation."
The commission's interpretation of the RIA requirements is also supported
by a change made to the APA by the legislature in 1999. In an attempt to limit
the number of rule challenges based upon APA requirements, the legislature
clarified that state agencies are required to meet these sections of the APA
against the standard of "substantial compliance." under Texas Government Code, §2001.035.
The legislature specifically identified §2001.0225 as falling under this
standard. The commission has substantially complied with the requirements
of §2001.0225.
Therefore in addition to not exceeding an express standard set by federal
law, these rules do not exceed state requirements, and are not adopted solely
under the general powers of the agency because the provisions of the TCAA, §§382.011,
382.012, 382.017, 382.019, and 382.039 authorize the commission to implement
a plan for the control of the states air quality, including measures necessary
to meet federal requirements. The remaining applicability criteria, pertaining
to exceeding a delegation agreement or contract between the state and the
federal government does not apply. Thus, the commission is not required to
conduct an RIA as provided in Texas Government Code, §2001.0225.
BCCA, BFI, ExxonMobil, Phillips 66, and WM commented that the rules were
proposed without an adequate takings impact assessment (TIA). BFI commented
that the agency failed to perform a meaningful TIA. BCCA, ExxonMobil, and
WM stated that Chapter 2007 of the Texas Government Code requires an agency
to prepare a written TIA when proposing a rule. BCCA, ExxonMobil, and WM further
stated that the assessment must describe the purpose of the proposed action;
determine whether engaging in the proposed action will constitute a taking;
and describe reasonable alternative actions that could accomplish the specified
purpose and explain whether these alternatives actions also would constitute
a takings. BCCA commented that these rules will significantly impact private
real property by rendering existing non-road equipment unusable. BCCA and
ExxonMobil stated that guidelines from the attorney general direct an agency
to carefully review governmental actions that have a significant impact on
the owner's economic interest. Finally, BCCA commented that commission did
not explain why the rules were reasonably taken to meet the federal requirement
and therefore does not qualify for the exemption claimed. BCCA stated that
these rules require more than is necessary to meet the federal requirement.
The primary reason the commission determined that these rules did not constitute
a takings under Texas Government Code, Chapter 2007 is that they will not
burden private real property. These rules apply to non-road equipment which
is not real property nor an appurtenance thereto.
In its analysis, the commission also found that the rules are exempt from
Texas Government Code, Chapter 2007 under §2007.003(b)(4), because they
are reasonably taken to fulfill an obligation mandated by federal law. The
commission included elsewhere in this preamble its reasoned justification
for adopting this strategy and explained why it is a necessary component of
the federally mandated SIP. This discussion, as well as the HGA SIP which
is being adopted concurrently, explains in detail that every rule in the HGA
SIP package is necessary, and that none of the reductions in those packages
represent more than is necessary to bring the area into attainment with the
NAAQS. This rulemaking action therefore meets the requirements of §2007.003(b)(4).
Although the rule amendments do not directly prevent a nuisance or prevent
an immediate threat to life or property, they do prevent a real and substantial
threat to public health and safety and significantly advance the health and
safety purpose and therefore meet the requirement of §2007.003(b)(13).
For these reasons the rules do not constitute a takings under Chapter 2007
and do not require additional analysis.
BCCA, ExxonMobil, PHA, Phillips 66, and WM stated that the proposed rules
did not include adequate notice as required under Texas Government Code, §2002.024.
ExxonMobil commented that §2002.024 requires that the notice of a proposed
rule include: a brief explanation of the proposed rule; its text; a statement
of the statutory or other authority for the proposed rule; a fiscal note showing
its impact to state and local governments; a note about public benefits and
costs; the local employment impact statement (if required); a request for
comments from any interested person; and other statements required by law.
BCCA, ExxonMobil, PHA, and WM stated that adequate notice is essential for
fairness as well as a meaningful opportunity to comment on a proposed rule,
and that courts have considered notice "adequate" only if: 1) interested persons
can confront the agency's factual suppositions and policy preconceptions;
and 2) the agency provides interested parties the opportunity to challenge
the underlying factual data relied upon by the agency. BCCA, PHA, and WM commented
that §2001.024 of the APA requires adequate notice of a proposed rule,
including information about its public benefits and costs.
BCCA, Phillips 66, and WM stated that they have identified a number of
critical gaps in the underlying factual data, methodology, and analysis in
support of the proposed rules. The commenters asserted that the proposal included
insufficient information and analysis regarding costs and impacts. The commenters
asserted that the commission has not adequately responded to requests for
additional information from stakeholders. The commenters stated that the following
requests for information were outstanding: information regarding the modeling
of emissions, information regarding the corrected emissions inventory database,
and information supporting the estimated costs of control. The commenters
stated that this information is necessary in order to comment effectively
on the proposed rules and that data gaps in the proposal hindered effective
comment.
The commission disagrees with the commenters and made no change in response
to these comments. Texas Government Code, §2001.024 requires that the
notice of a proposed rule to include certain information. Subsection (a)(5)
requires that the notice state the public benefits expected as a result of
the adoption of a proposed rule and the probable economic cost to persons
required to comply with the rule. Adequate notice is essential for fairness
as well as a meaningful opportunity to comment on a proposed rule.
United Loans, Inc. v. Pettijohn
, 955 S.W.2d 649, 651 (Tex. App.-Austin
1997). To achieve the goal of encouraging meaningful public participation
in the formulation and adoption of rules by state agencies, the notice must
have sufficient information so that interested persons can determine whether
it is necessary for them to participate in order to protect their legal rights
and privileges. The proposed rules contained an analysis of information available
to the commission regarding the costs and benefits of these rules. The commission
received intelligent comments which were substantial in both number and in
scope, regarding the costs as well as the benefits. Therefore, the commission
believes this goal has been achieved and that the notice includes sufficient
information to constitute adequate notice.
The purpose of the comment period is for the public to provide the commission
with information to say why they agree or disagree. There is no requirement
that the commission determine the probable economic cost of the unique aspects
of every facility or source that must comply, nor give the probable economic
cost of every possible method of control. Rather, the notice must include
the cost of a reasonable method of compliance. Mere disagreement with cost
estimates does not render notice inadequate.
These rules meet the requirement to include sufficient information in explaining
the fleet requirements, to whom they apply, the compliance schedule, the anticipated
cost of compliance, and the anticipated reduction in emissions. To simply
state that the proposal failed to provide sufficient information does not
provide the commission with sufficient information to propose changes or alternative
strategies. The commenters did not say how the notice is insufficient, merely
that it is insufficient. Nevertheless, the commission reviewed the notice,
determined it to be adequate, and responded to comments regarding costs associated
with compliance with these rules elsewhere in this ANALYSIS OF TESTIMONY.
Similarly, the comments which state there are critical gaps did not identify
what those gaps are or how that results in inadequate notice. The commission
is unaware of any requests for additional information to which it was not
completely responsive.
BCCA, ExxonMobil, PHA, Phillips 66, and WM commented that the rules were
proposed without an adequate small and micro-business assessment. Specifically,
the commenters stated that the commission failed to consider the costs of
compliance for small and micro-businesses, and that the proposal did not adequately
compare of the cost of compliance for small businesses to the cost of compliance
for the largest businesses affected by the proposed rules. The commenters
stated that Texas Government Code, §2006.002, requires an agency to prepare
a statement in the rule proposal of the effect on small and micro-businesses.
The commenters further stated that this statement must include an analysis
of the cost of compliance with the rules, and a comparison of the cost of
compliance for small and micro-businesses with the cost of compliance for
the largest business effected by the rules. The commenters stated that this
comparison must use one of the following standards: cost for each employee,
cost for each hour of labor, or cost for each $100 of sales. BCCA noted that
none of the SIP rules' small and micro-business assessments applied the mandated
cost comparison standards, even where the commission acknowledged "significant"
impact. BCCA commented that the commission either restated the costs of compliance
it identified in the analyses of public benefits and costs, or concluded that
it cannot determine the cost to small businesses. BCCA noted that it is impossible
for the public to provide comment on whether the commission adequately considered
the effect of the rules on small business because the commission did not publish
the information required by Texas law. Finally, ExxonMobil commented that
an agency must provide a basis for its conclusion that a rule does not adversely
impact small business and compare the impact on large versus small business.
The commission estimated, to the extent possible, the costs to small businesses
and determined that the cost depends more upon the number of non-road engines
operated by the business, and that it is not dependent upon the number of
employees, hours of labor, or amount of sales income. Some small businesses
have only one piece of non-road equipment while others have large fleets.
Large businesses vary in the same way. The size of the fleet is not dependent
upon the size of the business. The commission provided the estimated cost
per piece of equipment and argues that this is the only meaningful way to
provide sufficient notice of the cost to small business, and therefore, that
it meets the objective of the Texas Government Code, Chapter 2006. This assertion
is supported by the fact that no small businesses provided comments which
include cost of compliance in terms of the number of employees, hours of labor,
or amount of sales income.
BCCA, ExxonMobil, PHA and WM commented that the rules did not include the
local employment impact statement required under Texas Government Code, §2001.022.
The commenters stated that §2001.022, requires the commission to determine
whether the rule proposal has the potential to affect a local economy before
proposing the rule for adoption. The commenters stated that if answered affirmatively,
the commission must request that the Texas Workforce Commission (Workforce
Commission) to prepare a local employment impact statement describing in detail
the probable effect of the rules on employment in each geographic area affected
by the rule for each year of the first five years that the rules will be in
effect. The commenters further asserted that the commission failed to make
the required initial determination and ignored the potential for the proposal
to adversely affect the local economy. The commenters stated that a local
employment impact statement should have been requested and prepared in advance
of the proposal.
The commission agrees with the commenters that the rules may affect a local
economy, however, does not agree that it is the responsibility of the commission
to provide the local employment impact analysis. The APA requires state agencies
to determine whether a rule may affect a local economy before proposing a
rule for adoption. If an agency determines that a proposed rule may affect
a local economy, the agency must send a copy of the proposed rule and other
information to the Workforce Commission before the agency files notice of
the proposed rule with the secretary of state. The APA requires the Workforce
Commission to prepare a local employment impact statement for proposed rules,
if a state agency requests the statement. The commission determined that the
proposed rules might affect a local economy, and sent the proposed rules and
other requested information to the Workforce Commission. This commission received
a letter from the Workforce Commission, indicating that they did not have
the ability to determine the potential local employment impacts from the proposed
rules.
AGC-Texas, ARTBA, BCCA, BFI, EMA, PHA, Simonton, Spring Valley, WM, and
two individuals commented on federal preemption. One individual commented
that the rules may be preempted by federal regulations. Another individual
and Spring Valley commented that any attempt by the commission to adopt a
rule governing the emissions of non-road diesel engines is preempted by federal
law. ARTBA, BCCA, BFI, and PHA commented that the FCAA, §209 preempts
the commission from adopting these rules. BFI further stated that the Supremacy
Clause of the United States Constitution preempts the commission from adopting
these rules. AGC-Texas and BCCA commented that §209(e)(1) preempts states
from regulating new non-road engines in construction equipment/vehicles and
farm equipment/vehicles smaller than 175 hp. AGC-Texas and WM commented that
the rule language in 30 TAC §114.472 expressly requires fleets to meet
engine "standards" and that these standards exceed federal standards because
federal standards do not apply to used engines. AGC-Texas and WM further commented
that §209(e)(2) authorizes California to adopt and enforce "standards
and other requirements relating to the control of emissions," but other states
are not allowed to adopt new or used engine standards. Finally, AGC-Texas
commented that states must adopt California's non-road standards if they wish
to control new or used non-road engines not preempted by §209(e)(1),
and at this time California has not adopted used non-road engine standards.
EMA commented that §209(e)(2) broadly preempts all states and their political
subdivisions (except California) from adopting or attempting to enforce "any
standard or other requirements relating to the control of emissions" from
non-road engines and vehicles (42 USC, §7543(e)). EMA further commented
that preemption applies to all non-road engines and vehicles, whether they
are>
the sale and operation if Tier 1 non-road engines and vehicles that are otherwise
authorized for sale and operation under controlling federal law, and that
this would constitute a standard or other requirement relating to the control
of emissions from non-road engines. Simonton commented that the commission
should have no authority to tell owners of diesel equipment when to retire
equipment.
The commission disagrees that these rules are preempted by federal law.
The mobile source provisions of 42 USC were written to protect manufacturers
against a patchwork of different state standards. See
Engine Manufacturers Association v. EPA
, 88 F.3d 1075, 1079 (D.C. Cir.
1996). In accordance with the court's interpretation, only standards which
apply to the non-road vehicles or engines are preempted by the FCAA, §209(e).
States retain authority to promulgate in-use restrictions. Under this rule,
no manufacturer will have to create a special vehicle for Texas which is what
Congress intended to prohibit. The EPA established the existing standards
for non-road engines. These rules do not set a standard for non-road engines,
but instead they require that certain percentages of a non-road fleet meet
the existing federal Tier 2 and Tier 3 standards. Additionally, these rules
do not set a standard for in-use engines, they simply restrict the use of
older, dirtier engines within the HGA nonattainment area. This type of use
restriction is clearly allowed by the EPA rule for state implementation and
case law regarding preemption under §209(e). See 59 Fed. Reg. 36, 969
(July 20, 1994) and
Engine Manufacturers Association
v. E.P.A.
, 88 F.3d 1075 (D.C. Cir. 1996). The commission disagrees
with the comment which characterizes these rules as a standard instead of
a use restriction. The rules do not attempt to regulate or "ban" the sale
of Tier 1 equipment. The rules place no restrictions on the sale of equipment,
only the area of use. Tier 1 equipment may be used outside the nonattainment
area or it may be used in the area if the operator choose to comply with an
alternative plan for emissions reduction. In fact, the reductions required
by these rules do not have to be created by the equipment owner or operator
but may be acquired from other entities, by the purchase of credits through
the cap and trade program established in a concurrent rulemaking action. For
these reasons, these rules are not preempted by federal law.
An individual, AGC-Texas, and HCIC commented on legal authority. The individual
stated that the commission broadly interpreted the TCAA to give them the authority
to regulate non-road diesel engines. The individual further stated that the
commission authority is limited to on-road vehicles, and that it is not reasonable
to believe or infer that the Texas Legislature intended to directly confront
the FCAA and to usurp the EPA's direct responsibilities. AGC-Texas commented
that proposal of these rules exceed the commission's statutory authority.
AGC-Texas commented that TCAA, §382.09, applies "to engines used to propel
land vehicles" and that this section does not apply to "equipment" or engines
used not only to propel, but also to perform other functions. AGC-Texas commented
further that the prime function of the equipment covered by these rules is
not that of a land vehicle, and that this point is further reinforced by the
definition a motor vehicle in Texas Transportation Code, §114.500(2).
AGC-Texas concluded that these rules are therefore based solely on the general
powers of the agency. HCIC questioned the legal ability of the agency to write
and implement these rules.
The commission assumes that AGC-Texas is referring to TCAA, §382.019
as opposed to 382.09. In addition to §382.019, the commission also cites
authority in §§382.011, 382.012, 382.017, and 382.039, all of which
provide specific authority for this rulemaking, and are not "general powers"
of the agency. Section 382.019 specifically authorizes rules to reduce emissions
from engines used to propel land vehicles. As noted by AGC-Texas, engines
subject to this rule are used, at least in part, to propel the equipment.
The statute doesn't limit the commission's authority to engines which are
used solely or primarily to propel engines. Therefore the commission asserts
that §382.019 does provide authority for the adoption of these rules.
Additionally, the presence of this authorization does not imply a lack of
authority to control emissions from other types of vehicles or equipment.
For these reasons, the commission disagrees that this rulemaking exceeds its
statutory authority.
ABC commented that it is their understanding that Texas Health and Safety
Code, §392.011(b) directs the commission to seek to implement the TCAA
through measures that are "practicable and economically feasible." ABC stated
that these rules are anything but economical and feasible. BFI commented the
rules violate the TCAA in that the commission failed to conduct an analysis
sufficient to determine the economic feasibility of the rules and the public
health and general welfare impacts of those rules as required by TCAA, §§382.011 &
382.002. AGC-Texas commented that this strategy is not economically feasible.
These rules as proposed anticipated the possibility that some regulated
entities may find it difficult to replace their diesel equipment in accordance
with the schedule in the rules. Therefore the rules include a provision which
would allow the owner or operator to propose an alternative strategy to achieve
equivalent reductions. If there is a more cost-effective way to achieve the
necessary reductions, these rules allow for it to be implemented instead of
the fleet requirements. This provision of the rules ensures that the requirements
are practical and economically feasible. In the event that no other alternative
is more cost effective, then compliance with the fleet requirements is the
most practical and economically feasible way to make the reductions necessary
to meet the federal air quality standards.
Cost of compliance and equipment availability
ABC, AGC-Texas, ARTBA, BFI, Chambers County, Harris County, HCIC, Texas
City, Spring Valley, Missouri City, and six individuals commented on the financial
impact of these rules. One individual commented that the cost of new equipment
must be borne by the public in the case of equipment used by industry and
the taxpayer in the case of government work and equipment. Another individual
commented that these rules will economically devastate small and marginal
construction companies. The third individual commented that the people should
not be forced to do things, plus people cannot afford it. The fourth individual
commented that the rules would greatly add to the city operating and capital
costs. The fifth individual commented that these rules will bankrupt businesses.
The sixth individual commented that the rules will cause small business owners
to find a way to get around the rules by being dishonest, or if he does follows
the rules, then he will be forced out of business by the cost of replacing
equipment. Chambers County questioned if the rules are going to shut their
construction and economic development down. HCIC and Harris County commented
that they oppose the rules for economic reasons. ARTBA commented that small
businesses, minority-owned construction companies, and minority and low-income
workers will be impacted by these rules. ARTBA further stated that the rules
will impose huge capital costs on construction companies. AGC- Texas commented
that contractors will have to borrow $4.5 billion in order to comply with
these rules and that this amount of debt can not be absorbed by the industry.
ABC commented that contractors will be seriously damaged economically if they
are forced to purchase new equipment before the lifespan of their equipment
has been reached. They further commented that cost of these rules to the construction
industry, along with the workday shift rules, would be around $450 million
for the eight- county area. Texas City commented that the rules will result
in an increase of equipment cost which will make it harder for smaller communities
and school districts to comply with the rules. Missouri City commented that
increased costs with city construction projects could result.
The commission recognizes that compliance with these rules will result
in increased costs and economic impacts to affected businesses and the communities
in which these businesses operate. However, the commission anticipates that
affected companies and communities will find and make the necessary adjustments
to minimize these impacts, especially considering the far more substantial
economic impacts that would result from the failure of the HGA area to attain
the federal air quality standards that these rules are designed to help achieve.
These rules are an essential component to the overall strategy to reduce peak
ozone levels to enable the HGA area to attain federal ozone standards. Although
many of the rules included in the current SIP attainment strategy will not
be easy to implement and will cause many of the affected entities to adjust
normal operations and make certain sacrifices, these rules are of critical
importance in the protection of the environment and human health, which is
essential for continued economic prosperity for all entities affected by the
rules. The failure to attain these standards would significantly impact the
area's economy, and the quality of life of its citizens and communities.
In order to provide maximum flexibility, the rules includes a provision
for an emissions reduction plan. This is a plan submitted to the commission
by a fleet owner or operator to show alternate methods of achieving emissions
reductions equivalent to the emissions reductions that would be achieved by
complying with the requirements of these rules. This provision will allow
for the financial impacts to industry and governments to be mitigated if they
find ways to achieve the emission reductions without having to buy new equipment.
ABC, BCCA, and Dow commented on federal Tier 2/Tier 3 equipment availability.
ABC and BCCA commented that the commission is requiring owners and operators
to have Tier 2 and Tier 3 engines and equipment earlier than the federal schedule.
ABC commented that the accelerated implementation of the Tier 2 and Tier 3
engines may not be possible given that many of the nation's engine manufacturers
are only planning their rollout of Tier 2 and Tier 3 engines based on the
FCAA schedule. BCCA commented that the rules impose a duty on owners and operators
to have in place, engines that meet Tier 2/3 standards on a schedule that
is earlier than the federal standard. Dow commented that they can not determine
if Tier 2 or Tier 3 equipment is available or if it will become available
by the effective date of these rules.
These rules do not accelerate the implementation of the Tier 2 and Tier
3 engines as set forth in 40 CFR, §89.112. The rules simply require that
a fleet owner or operator ensure that their fleet consists of Tier 2 and Tier
3 engines as specified in §114.472. In essence, these rules accelerate
the natural turnover of the equipment. All manufacturers who plan to keep
selling non-road diesel engines in the United States will already have to
comply with the Tier 2 and Tier 3 standards. At this time, the commission
is unaware of any manufacturers that are not going to sell Tier 2 and Tier
3 engines. Furthermore, the requirement dates in the rules were determined
so that they come after the federal implementation dates of the Tier 2 and
Tier 3 engines. In other words, if a owner or operator of a fleet chooses
to buy new non-road equipment to comply with these rules, then this equipment
will already be on the marketplace. The following table contains the implementation
dates of the federal Tier 2 and Tier 3 standards.
Figure 2: 30 TAC Chapter 114 - Preamble
For example, the rules as adopted require non-road equipment fleets in
the 100 to 750 hp range to be 10% Tier 2 by the end of 2004. Tier 2 engines
are available beginning in years 2001 to 2003 for this hp range. Thus the
rules are not requiring use of the equipment until it is available on the
marketplace.
An individual, NASA, PHA, and WM commented on the compliance schedule.
The individual asked that more time be given in the compliance schedule. NASA,
PHA, and WM commented that they are concerned that the transition to lower
emission diesel engines may not be achievable due to production limitations
of the original equipment manufacturers (OEM), and NASA encouraged the commission
to work with the OEMs to ensure a realistic schedule. Furthermore, PHA suggestd
that, if the commission does pursue this rule, then in order to address the
engine availability issue, PHA requested that an exemption be added to §114.477
as follows:
(c) An operator is exempt from complying
with §114.472 and §114.476, if it can demonstrate that no equipment
that can perform the function of the equipment to be replaced and that meets
the Tier 2 and Tier 3 standards is commercially available.
The commission disagrees that an exemption as outlined by PHA should be
added to the rules. Furthermore the commission believes that the compliance
schedule is long enough to ensure adequate supply. The commission expects
that the adoption of these rules and the subsequent demand that will result
from the adoption will prompt the manufacturers to make sure that they can
meet the demand. Also, if fleet operators or owners submit emissions reduction
plans, that are approved by the commission, then the demand for the equipment
may not be as great since there will be other alternatives to achieve the
emissions reductions.
MCA commented that rules such as the construction ban will not be effective.
MCA stated that accelerating the phase-in schedule of these rules would provide
the additional NO
x
reductions that would purportedly
be gained from the construction ban.
The commission believes that the "construction ban" will be effective rules.
Furthermore, it is not possible to accelerate the phase-in schedule any more
than what is already in the rules because the requirement dates in the rules
were established so that they come after the federal implementation dates
of the Tier 2 and Tier 3 engines. In other words, if a fleet owner or operator
chooses to buy new non- road equipment to comply with the rules, then this
equipment will already be on the marketplace. The commission believes that
the compliance schedule is as aggressive as possible given these considerations.
An individual commented that the commission should require California heavy
equipment engines on new equipment as of October 1, 2003.
The commission disagrees with this comment. California has adopted the
federal Tier 2 and Tier 3 standard for non-road engines. Therefore requiring
California engines would achieve the same benefit as requiring a federal engine.
Furthermore, the commission disagrees with using October 1, 2003 as a start
date because Tier 2 engines with hp greater than or equal to 50 and less than
100 and engines with hp greater than 750 will not be on the market yet. No
changes have been made to the rule in response to this comment.
An individual commented that the rules go far beyond anything that is necessary
to protect the environment, that the analysis and basis behind these rules
is flawed, and that these rules are being set up to embarrass Texas and the
Governor.
The commission's intent is not to embarrass Texas and/or the Governor but
instead to comply with the timelines provided in 42 USC and subsequent EPA
guidance for submitting rules to demonstrate ozone attainment in HGA. Accordingly,
the commission has committed to adopting the majority of the necessary rules
for the HGA attainment demonstration by December 31, 2000.
The commission worked extensively with the construction industry and other
affected industries in the HGA area, along with consultants, to ensure that
the emissions inventory and the inventory of affected equipment in the area
is as accurate and as specific to the HGA area as possible. The accuracy of
the inventories thereby ensures the accuracy of the modeling of the affected
industries' contribution to the air quality problem, as well as the necessary
ozone reductions that these rules are designed to achieve. The commission
is required to use a federally-recognized and approved model for developing
data that will be used to demonstrate attainment with the SIP. The commission
used the most state-of-the-art photochemical methodologies to develop these
rules. The Comprehensive Air Model with Extensions (CAMx) model that was used
is the latest version of the photochemical model for SIP modeling recognized
by the EPA. The Houston Diesel Construction Emissions project was conducted
with the goal of improving upon the emission levels used previously in the
Houston attainment plan. Previous inventories had been supplied by the EPA
in their Non-Road Equipment and Vehicle Emission Study (NEVES). As such, the
accepted method to model years other than the 1990 NEVES data was to apply
growth factors from the Economic Growth Assessment System (EGAS); then technology
reduction factors had to be applied to the grown inventories to model new
federal emission rules such as those for diesel engines. Over the last year,
however, a new method of calculating non-road emissions has been developed
by the EPA called the NONROAD model. The NONROAD model will be used for updating
the attainment modeling (1993 base case and 2007 future case) for the Houston
area because the model has the best available science with regard to emission
factors and treatment of activity (equipment usage rates) data. The NONROAD
model works more like the highway emissions model, MOBILE, in that temperatures
and fuel qualities can be modified to better reflect local conditions. The
main change to the NONROAD model input stream was the use of new equipment
populations for diesel construction equipment. The commission worked with
representative construction operators through independent engineering firms.
The general approach was to define the market share of the representative
construction companies and then upscale the equipment totals based upon estimated
total market share. Local equipment data then had to be adjusted to state
equipment populations using adjustment factors, because NONROAD requires state-wide
totals to perform the county-based calculations. Under contract with the Houston-Galveston
Area Council (HGAC), Eastern Research Group (ERG) conducted a detailed survey
of construction equipment populations and activity within the eight-county
HGA ozone nonattainment area. As part of this effort, Starcrest Consulting
facilitated communications with a coalition of local construction trade organizations
and assisted with the development of survey strategies. Based on the study's
findings, input files were generated for use in the EPA NONROAD emissions
model in order to estimate total pollution levels from construction sources
operating in the area. These results serve as an update to the commission's
previous estimates based on the EPA's default methodology. Commission staff
then re-ran the NONROAD model using the revised input files to develop a revised
construction emissions inventory for the Houston area. For several reasons
it is believed that the NEVES survey methodology originally used significantly
overestimated equipment populations (and therefore emissions) for the construction
sector in Houston. For example, Houston serves as headquarters for some of
the world's largest construction companies, with thousands of employees dedicated
to engineering and administrative work. However, the employment surrogates
found in the County Business Patterns Report do not distinguish between "office"
and "field" employees. While the number of construction field employees in
a given area may be indicative of overall construction activity, projections
using total "construction employment" in the Houston area may drastically
overestimate overall equipment numbers and activity. For these reasons it
was thought that a "bottom-up" survey of construction sources in the area
could provide significant improvements to the equipment inventory. However,
previous survey attempts encountered very low response rates, and ultimately
proved unsuccessful. As part of a multi-task contract with HGAC, ERG agreed
to perform a comprehensive survey of all construction equipment activity in
the eight-county HGA ozone nonattainment area. In order to improve survey
response rates, ERG obtained assistance from a coalition of several local
trade organizations, termed the HCIC. The HCIC, along with their representative
Starcrest Consulting, was instrumental in identifying key experts for interviews,
as well as encouraging their member companies to actively participate in the
survey effort. This effort provided the commission with a much-improved inventory
of construction equipment emissions in the Houston area, and resulted in the
revisions incorporated into the Base 6 and Base 6a modeling. Even though the
revised inventory greatly reduced the uncertainty in construction equipment
emissions, the commission continually seeks to improve its inventories.
Based upon this in-depth work, the commission believes that the analysis
and basis behind the rules is not flawed. Additionally, the SIP modeling makes
clear that the SIP does not require more reductions than are absolutely necessary.
Alternatives and Flexibilities
Two individuals, Baker Botts, AGC-Texas, BCCA, Dow, and Spring Valley commented
on the need for the EPA to implement the Tier 2 and Tier 3 standards sooner
that what is currently prescribed, and to be held accountable for their lack
of timely action on non-road engines. One individual and Spring Valley commented
that the commission should engage in discussion with the EPA to encourage
the earlier implementation of these standards. The second individual, Baker
Botts, and PHA commented that the commission should urge the EPA to grant
SIP consideration based on their lack of timely action. AGC of Texas commented
that the EPA should accept responsibility for the late promulgation of federal
standards for non-road engines. They commented that this has caused the commission
to consider onerous strategies with regard to these engines that are not economically
feasible. Baker Botts commented that it generally supports the ongoing efforts
by the commission to develop a SIP that is technologically achievable, economically
reasonable, and legally approvable. Baker Botts, BCCA, ExxonMobil, Harris
County, Phillips 66, Spring Valley, and an individual commented that the commission
should incorporate into the SIP a greater level of reductions from federally
preempted sources and stated that EPA-regulated sources account for about
40% of the NO
x
emissions in the HGA. The commenters
stated that the EPA issued a number of regulations for some federally preempted
sources, such as land-based spark engines, marine, recreational and land-based
diesel engines, aircraft, and locomotive engines, well after the FCAA deadlines,
and that the EPA recently strengthened rules for on-road and non-road vehicles
and fuels, such as low sulfur gas and diesel, Tier 2 motor vehicles, heavy-duty
highway vehicle standards, and non-road Tier 2/Tier 3 heavy-duty engine standards.
The commenters stated that delays in implementing these rules have prompted
the commission to propose technically and economically infeasible emission
reductions from sources in HGA that the state has authority to regulate to
make up for the missing federal reductions. The commenters stated that these
delays have forced the commission to propose expensive regional fuels and
significant use restriction regulations. The commenters stated that the commission
and the EPA can ensure an equitable distribution of the compliance burdens
necessary to meet mandated air quality improvement in HGA only by allowing
the SIP to capture anticipated emission reductions from federally preempted
sources. Baker Botts noted that the EPA demonstrated a willingness to assume
responsibility for a portion of emission reductions by creating a process
in Los Angeles called a "public consultative process," that would resolve
issues related to emissions from national and international sources, and that
the EPA has also provided flexibility in obtaining offsets by allowing states
to provide offsets to refiners based on emission reductions that the EPA projected
would result from mobile sources using Tier 2 gasoline. Baker Botts suggested
that this same sort of prospective crediting should be used to develop a more
rational HGA SIP, and that the EPA should allow the commission to credit in
the SIP the prospective emission reductions that will result from implementation
of the Tier 2 gasoline rule and from other federally preempted sources. Finally,
Baker Botts cited two cases in which the District of Columbia Circuit Court
has approved the EPA's flexibility with respect to statutory deadlines under
the FCAA when the EPA has failed to meets its own deadlines, and this failure
was deemed to upset the balanced federal/state responsibilities under the
FCAA. ExxonMobil commented that it supports the commission and the EPA crediting
the HGA SIP with an additional 60 tpd of federally preempted emission reductions
that will occur over the next ten years. Harris County commented that the
commission should work with the EPA to accelerate the implementation schedule
for federally preempted emissions so that at least one-half of the related
emission reductions are achieved by 2007, and that as a part of this process,
the commission should delineate federal assignments detailing the engine standards
and emission reductions necessary to achieve real and sustainable pollution
reductions.
The commission agrees with the commenters that emission reductions from
federally preempted sources would provide benefits for the HGA SIP demonstration,
and the inability of the commission to regulate certain source categories
has necessitated the use of other ozone control strategies. However, the commission
understands that the EPA SIP approval process does not provide a mechanism
for credit for emission reductions that occur after the attainment date. The
commission understands that the EPA is not currently considering accelerating
implementation schedules for existing federal rules. The commission is working
with the EPA to determine the availability of SIP credit for many nontraditional
control strategy mechanisms, like economic incentive programs and flexibility
for preempted source categories. Additionally, the commission is working with
the EPA to determine an appropriate federal contribution credit available
for the HGA SIP.
WM commented that the commission should explore other alternatives such
as the extension of the attainment deadline in order to provide sufficient
time for new, low-emission equipment to penetrate the market.
The FCAA requires that a state have no more than one exceedance of the
NAAQS in the year preceding the extension year, and that the state has complied
with all requirements and commitments in the applicable implementation plan,
prior to EPA granting such an extension. There is no provision in the FCAA
or EPA guidance for EPA granting an extension in the absence of this data.
However, the commission is committed to working with EPA and all interested
parties to provide opportunities for new, low-emission equipment availability
within the HGA nonattainment area.
Two individuals requested that the mandatory element of this rule be deleted
to allow for a voluntary program. Another individual commented that the rule
should be voluntary on equipment predating 1992. The Mayor of Houston urged
the commission to work with industry to try to develop voluntary agreements
in order to avoid lawsuits.
The EPA provides for the inclusion of voluntary programs or measures as
part of the attainment demonstration, but limits the amount of emission reduction
credit that may be claimed from such measures, due to the fact that the programs
are not enforceable mechanisms. In accordance with EPA policy, the commission
included some voluntary programs as part of the HGA SIP. The HGAC is the entity
responsible for the development and implementation of these programs, which
are detailed in the HGA SIP as the Voluntary Mobile Emissions Reduction Program
(VMEP). If the adopted rule became voluntary it could not be counted as an
enforceable measure obtaining emission reductions for the demonstration of
attainment. As stated elsewhere in this preamble, the emissions reductions
associated with these rules are necessary for the attainment of the NAAQS
in the HGA area. The NO
x
emissions from non-road
equipment comprise 12% of the HGA area's total NO
x
emissions. Because of this significant contribution that the equipment affected
by these rules makes to the HGA area's ozone levels, it is essential that
the rules be implemented along with the other rules and measures included
in this SIP revision in order for the HGA area to demonstrate attainment with
the federal ozone standard. It is possible for voluntary measures to be made
enforceable through agreements and in that case they can be counted toward
the SIP. The commission included a provision in these rules which would allow
these enforceable agreements to be counted toward compliance with the rules.
The commission encourages efforts to reach enforceable agreements as suggested
by the Mayor of Houston, and looks forward to working with all interested
participants.
Two individuals, ABC, AGC-Texas, BCCA, ED, ARTBA, Harris County, HCIC,
AGC- Houston, PHA, Spring Valley, Texas City, the Houston MPO, and WM commented
that the commission should provide for economic incentive programs to encourage
development of new technologies, achieve earlier and/or greater reductions
in pollution, and substitute for other rule proposals which may be costly
and difficult to meet and enforce. The first individual, Spring Valley, and
the Houston MPO commented that the rules should be replaced with an economic
incentive program. The second individual and WM commented that the commission
should consider voluntary rules that are part of an incentive program. ABC
and BCCA commented that a diesel equipment incentive plan should be developed
and that such plan would remove more NO
x
emissions
than both the construction workday shift rule and the accelerated Tier 2/Tier
3 rule combined. AGC-Texas commented that the commission should replace these
rules with a market-based incentive program similar to the California Carl
Moyer program. AGC-Houston commented that they support State Senator Buster
Brown's proposal of developing legislation to fund an incentive program patterned
after the Carl Moyer program in California. ED commented that the rules should
be supplemented with market-based strategies that can be implemented immediately.
The commission agrees that economic incentive programs can potentially
be an effective tool for achieving air quality. One such program is the Carl
Moyer program in California. That program appears to be successful in providing
flexibility to the regulated industry while still achieving reductions in
air emissions. The California program is authorized by and funded through
the California state legislative process; however, such legislative approval
does not currently exist for a similar Texas program. The commission will
continue to try to identify economic incentives which it has authority to
implement. Because the commission agrees that market-based incentive programs
can be an important component in encouraging development of new technologies
and/or greater or more cost-effective emission reduction strategies, the commission
has provided for the inclusion of economic incentive programs as a component
of the HGA SIP in the future.
In addition, these particular rules do provide for the regulated entity
to submit an alternative plan to achieve equivalent emission reductions. This
alternative would enable regulated entities to take advantage of an economic
incentive program which is developed in the future. The commission will continue
to work with industry representatives to identify options for compliance which
may currently exist or which may become available in the near future.
Three individuals commented that a tax credit or tax incentive should be
given to companies to help replace their equipment.
The commission agrees that a tax credit or incentive would be helpful.
Currently, 30 TAC Chapter 17, Tax Relief for Property Used for Environmental
Protection, is the commission's program that provides tax relief for the purchase
of pollution control property. On November 2, 1993, the Texas voters approved
a constitutional amendment, commonly referred to as "Proposition 2," that
provides an exemption from property taxation for pollution control property.
The intent of the constitutional amendment was to ensure that capital investment
undertaken to comply with federal, state, or local environmental mandates
did not result in an increase in a facility's property taxes. Legislation
implementing that amendment, House Bill 1920, was passed during the 73rd Texas
Legislative Session which added a new §11.31 and §26.045 to the
Texas Tax Code. The Tax Code provides that pollution control property could
include any land purchased after January 1, 1994; or any structure, building,
installation, excavation, machinery, equipment, or device; and any attachment
or addition to or reconstruction, replacement, or improvement of property
that is used, constructed, acquired, or installed wholly or partly to meet
or exceed rules or regulations adopted by any federal, state, or local environmental
agency for the prevention, monitoring, control, or reduction of air, water,
or land pollution. Motor vehicles are specifically noted as being ineligible
for an exemption under this provision of the Tax Code. The Tax Code contains
a two-step process for securing an exemption from property taxes for pollution
control property. An applicant must first receive a determination from the
commission that the property is used for pollution control purposes. The applicant
then can use this determination to apply to the local appraisal district for
a property tax exemption.
The Mayor of Houston commented that the Construction Trades Association,
EMA, and other interest groups are contemplating lawsuits for the purpose
of removing these rules, among others, from the SIP. However, the city recognizes
that without these rules, the area will not be able to meet the air quality
standards. Therefore the city urges the commission to begin dialogue with
the groups to develop enforceable alternatives. Texas City commented that
the city is working with various industry groups to try to identify flexibilities
for complying with the rules.
The commission agrees that these rules are needed for the HGA area to reach
attainment. In order to achieve the maximum flexibility possible, the rules
include a provision for an emission reduction plan. This is a plan submitted
to the commission by a fleet owner or operator to show alternate methods of
achieving emissions reductions equivalent to the emissions reductions that
would be achieved by complying with the requirements of these rules. To develop
a guidance document for this plan, a workshop has already taken place where
stakeholders were invited and were given drafts of the requirements of the
emissions reduction plan and asked for their input and comments. Further workshops
will be held and the commission intends to work with the stakeholders to come
up with an emissions reduction plan guidance document that will be workable
and agreeable to everyone. The commission appreciates the efforts of all local
entities, such as Texas City, which are working with industry to identify
options for compliance.
Rule Coverage
Sierra-Houston and one individual commented that the rules should be adopted
statewide.
The commission appreciates the support for state-wide applicability of
the rules. The commission notes, however, that it is not obligated to adopt
all rules statewide in order to satisfy its commitments under the SIP, nor
is the commission required to do so under 42 USC. Three of the proposed measures
which contained emissions reduction strategies that have been proposed for
state-wide applicability are: California large-spark ignition engines; emissions
banking and trading program (that portion of the rules which relates to the
trading of emission reduction credits and discrete emission reduction credits);
and cleaner diesel fuel (that portion of the proposed rules which relates
to on-road fuel).
In evaluating whether to implement all of the rules statewide, the commission
took into account many concerns, including the need for the marketplace to
be able to respond to regulation, the possible impacts on transport and distribution
systems, the possibility of increased costs and financial burdens on regulated
entities, and the regional needs and issues associated with state-wide mandates.
The commission analyzed where emission reduction measures are most needed
and where emissions reduction measures will be most effective in order to
demonstrate attainment.
Equipment inventories and emission inventories do not support the implementation
of these particular rules on a state-wide basis. These inventories and associated
modeling show that the vast majority of heavy-duty diesel equipment is located
and used in the DFW and HGA metropolitan areas, coinciding with the major
concentrations of population in the state. Therefore, emissions from this
equipment are also concentrated in those areas. In addition, these areas have
air quality problems that are more serious than the rest of the state, primarily
with ozone, the compound that these rules are designed to help reduce. These
existing air quality problems, coupled with the geographic concentration of
equipment usage and emissions, justifies implementing rules to control the
emissions of ozone-forming compounds from heavy-duty diesel equipment in the
DFW and HGA areas only, rather than statewide. Generally, mobile source emissions
have more of a localized effect on ozone formation than elevated point sources.
Given the more localized effect, and the fact that equipment subject to these
rules do not typically travel over long distances, a state-wide application
of the rules is not warranted at this time. However, these rules do not preclude
other areas from implementing similar locally-regulated or voluntary programs
to achieve similar benefits.
After careful consideration of all of these factors, the commission determined
that the rules as proposed will achieve the needed emissions reductions and
promote cleaner air throughout the State of Texas.
Montgomery Co. commented that their elimination from these rules would
result in a difference of less than 1/100th of one ppb (0.01 ppb) of ozone.
One individual commented that the rules such as this one should not apply
in rural counties like Chambers and Liberty Counties.
Montgomery, Chambers, and Liberty Counties are all part of the HGA nonattainment
area. The FCAA Amendments of 1990 provided new requirements for areas that
had not attained the NAAQS for ozone, carbon monoxide, particulate matter,
sulfur dioxide, nitrogen dioxide, and lead, and new requirements for SIPs
in general. The EPA was authorized to designate areas failing to meet the
ozone NAAQS as nonattainment and to classify them according to severity. The
FCAA, §107(d)(4)(A)(iv) mandated that areas designated as serious, severe,
or extreme for ozone that were within a metropolitan statistical area (MSA)
or CMSA must have boundaries that include the entire MSA or CMSA. This requirement
is supported by the legislative history for the FCAA Amendments in Senate
Report Number 101-228, page 3399, "Because ozone is not a local phenomenon
but is formed and transported over hundreds of miles and several days, localized
control strategies will not be effective in reducing ozone levels. The bill,
thus, expands the size of areas that are defined as ozone nonattainment areas
to assure that controls are implemented in an area wide enough to address
the problem." The FCAA provided the ability to exclude portions of the entire
MSA or CMSA prior to designation if the state conducted, and EPA agreed, a
study that proved that the geographic portion did not contribute significantly
to violation of the NAAQS.
For existing areas currently included within a nonattainment area, the
specific area must be redesignated as attainment in order to be removed from
a nonattainment area designation. FCAA, §107(d)(3) provides that the
EPA may not redesignate a nonattainment area, or a portion thereof, to attainment
unless several criteria are met, which include: a determination that the area
has attained the NAAQS; there is a fully approved SIP for the area; there
is a determination that the improvement in air quality is due to permanent
and enforceable reductions in emissions; there is an approved maintenance
plan for the area; and the state has met all requirements for the area under
Section 110 and Part D of the FCAA. Redesignation has not occurred for any
portion of the HGA nonattainment area, and is not currently being considered.
However, even if a specific area within the HGA nonattainment area was
redesignated by the EPA as attainment for ozone, reductions associated from
all adopted ozone control strategies would still be necessary because of the
requirements of the FCAA, §107(d)(3) and §175A which require maintenance
plans for all redesignated areas. The maintenance plan must include the measures
specified in §107(d)(3) and any additional measures that are necessary
to ensure that the area continues to be in attainment with the NAAQS for ten
years after the redesignation. Eight years after the redesignation, the state
is required to submit an additional revision to the SIP for maintaining the
NAAQS for another ten years after the end of the first ten-year period.
Additionally, reductions associated from the ozone control strategies that
will be implemented outside the HGA nonattainment area will benefit the HGA
nonattainment area. This is due to the regional nature of air pollution, the
contribution from mobile sources, and the economies of scale and associated
market advantages related to distribution networks for some strategies.
At the time the 1990 FCAA Amendments were enacted, the focus on controlling
ozone pollution was centered on local controls. However, for many years an
ever increasing number of air quality professionals have concluded that ozone
is a regional problem requiring regional strategies in addition to local control
programs. As nonattainment areas across the United States prepared attainment
demonstration SIPs, several areas found that modeling attainment was made
much more difficult, if not impossible, due to high ozone and ozone precursor
levels entering from the boundaries of their respective modeling domains,
commonly called transport. Recent science indicates that regional approaches
may provide an improved control of ozone air pollution.
The commission conducted air quality modeling and upper air monitoring
that found regional air pollution should be considered when studying air quality
in Texas' ozone nonattainment areas. This work is supported by research conducted
by the OTAG, the most comprehensive attempt ever undertaken to understand
and quanitfy the transport of ozone. Both the commission and the OTAG study
point to the need to take a regional approach to controlling air pollutants.
Five individuals commented that the rules would have an impact to farming
and ranching. Two individuals commented that farmers and ranchers could not
afford new equipment. Another individual commented that the rules would have
an adverse economic impact on farmers. The commenter further stated that a
project being undertaken by farmers in the Liberty, Jefferson, and Chamber
counties will make "carbon credits" available to local industries which will
not only have cash value but economic development advantage points. Three
individuals commented that the cost of new equipment would be prohibitive
and suggested that an agricultural exemption be put in place.
The commission disagrees that farmers and ranchers will experience a severe
economic impact because the rules already contain an exemption, in §114.477(a)(6),
for equipment which is used solely for agricultural purposes. This would include
much, if not all, the equipment used by farmers and ranchers. Therefore, the
rules would not affect farmers and ranchers unless they were using heavy-duty
diesel equipment for non-agricultural purposes. Concerning the project that
is being undertaken by the farmers, the commission supports all projects which
have a potential to reduce emissions and support economic development.
TFA and TLC commented that small businesses such as logging contractors
are not financially able to retire their equipment. They further state that
the rules would be devastating to these contractors.
The commission disagrees that loggers will experience a severe economic
impact because the rules do not require logging equipment such as chain saws,
shredders, fellers, bunchers, and skidders to comply with these rules. The
commission added language to the agricultural exemption to make clear that
logging uses are also exempt.
Rule Effectiveness
Simonton commented that the commission should limit their concern to the
exhaust emission levels, not the age of the equipment. An individual commented
that we should look at the quality of what the equipment is putting out instead
of just retiring old equipment. If the equipment is bad, then retirement may
be necessary.
These rules are in fact based upon the exhaust emissions, not the age of
the equipment. The rules require that certain percentages of a fleet must
be certified to meet federal standards. The rules do not prohibit use of older
equipment if it can be retrofitted to meet the same emission rates as newer,
cleaner equipment. Additionally, if an operator chooses to submit an emissions
reduction plan, older equipment may be included under that plan.
The commissions acknowledges that their may be old equipment that runs
fine and is properly maintained, and therefore its emissions are acceptable
for that equipment. However, the fact remains that the Tier 2 and Tier 3 engines
will have more stringent standards than previous engines and equipment. Therefore,
emissions levels will be lower for these fleets that contain Tier 2 and Tier
3 equipment or their equivalent.
An individual, Harris County, and the Houston MPO commented that the rules
will not be effective. The individual stated the proposal is not based on
proven technology, and Harris County stated that the rules are untried and
untested. The Houston MPO commented that the Tier 2/Tier 3 standards are experimental,
difficult to quantify, and market acceptance is uncertain.
The commission disagrees that these rules will not be effective. Although
it is true that this strategy has never been implemented, the commission believes
that it is reasonable, based on known and credible science, to reduce emissions
from diesel equipment in order to meet the federal ozone NAAQS. The federal
Tier 2 and Tier 3 standards are more stringent than Tier 1 and earlier equipment.
It is therefore reasonable to conclude that a fleet that consists of only
Tier 2 and Tier 3 equipment will emit less than a fleet that consists of a
mix of unregulated, Tier 1, Tier 2, and Tier 3 equipment. The commission disagrees
that market acceptance will be a problem because the Tier 2 and Tier 3 engine
standards are a federal requirement, and therefore the manufacturers will
have no choice but to produce such engines. The demand created by these rules
may actually increase sales of the newer equipment which could help manufacturers
recoup their development costs more quickly. The commission disagrees that
the rules will be hard to quantify because the emission factors for this equipment
are known and because the HGA inventory of construction equipment has been
significantly refined. Through the use of the NONROAD model and the photochemical
modeling, the rules have been shown to reduce 12.20 tpd of NO
x
in 2007. For these reasons the commission asserts that the rules
are based on well-accepted science and that they will be an effective emission
reduction strategy.
Miscellaneous
Sierra-Houston opposes the use of emission credits and trading for these
rules because they feel that the commission should be maximally reducing air
emissions. Dow supports the commission position to allow credits for early
upgrades to diesel equipment. Harris County supports the use of trading.
The commission disagrees that emission credit and trading should not be
used to help with compliance to the rules. The commission believes that the
flexibility offered through emission trading will provide opportunities for
regulated entities to achieve significant emission reductions in a method
that best suits that particular entity. This is just one tool that can be
used in the emissions reduction plan to get the needed emission reductions.
Furthermore, trading can only occur within the same nonattainment area so
when a credit is generated, an actual reduction is taking place in the HGA
nonattainment area. Finally, trading encourages early reductions and could
give incentive for the development of cleaner technologies on an accelerated
timetable.
Two individuals commented on the use of equipment after it has been "retired."
One individual commented that the retiring of old equipment that is inefficient
will result in such equipment ending up in third world countries such as South
America and Africa. The commenter suggested that the equipment be scrapped,
certified, and inspected. The second individual commented that this equipment
should be dismantled.
The commission agrees that the "retirement" of old equipment may cause
such equipment to end up in other areas of the region, state, nation, and
possibly the world. The commission anticipates that this older equipment will
be resold or transferred out of the area, thus mitigating the cost of compliance
with these rules. Use of this older equipment in areas which do not have air
quality problems is not cause for concern.
Concerning the dismantlement, scrappage, certification, and inspection
of the "retired" equipment, the commission believes that the equipment should
not be scrapped, because that equipment can be used in other areas outside
of HGA. Furthermore, the commission does not believe certification and inspection
of this "retired" equipment would serve any useful purpose.
Two individuals, Sierra-Houston, and Liberty County-Sheriff expressed concern
over enforcement of the rules. More specifically, Sheriff Arthur wondered
who is going to enforce the rules. He stated that they have a lot more serious
problems in Liberty County to be concerned about. Sierra-Houston commented
that the commission has not explained how enforcement will be done.
As with all of its rules, the commission will enforce the requirements
after the rule compliance date and take appropriate action for noncompliance
situations. The rules are enforced by commission staff in the regional offices,
as well as local air pollution control programs. Local governments have the
same power and are subject to the same restrictions as the commission under
TCAA, §382.015, Power to Enter Property, to inspect the air and to enter
public or private property in its territorial jurisdiction to determine if
the level of air contaminants in an area in its territorial jurisdiction meets
levels set by the commission. Local governments are not required to enforce
commission rules, but may sign cooperative agreements with the commission
to enforce the rules under TCAA, §382.115, Cooperative Agreements. Local
programs can also enforce commission rules without signing a cooperative agreement.
The authority of local governments to enforce air pollution requirements is
specified in detail in TCAA, §§382.111 - 382.115, and local governments
can institute civil actions in the same manner as the commission under Texas
Water Code (TWC), §7.351.
The commission will work with local officials to ensure enforcement of
the SIP and SIP rules. The commission has existing relationships with pollution
control authorities in the City of Houston, Harris County, and Galveston County
for enforcement of other commission rules. The agency will continue enforcement
relationships with these entities and develop relationships with other local
officials as needed to create effective enforcement mechanisms for the SIP
and SIP rules.
Effected entities are required to report in accordance with 30 TAC §114.476,
Reporting and Recordkeeping Requirements, and would have to keep those reports
onsite. These rules have been written to allow enforcement to take place during
operation by an investigator who requests the reports. An operator without
reports on-site which include the piece of equipment being operated can then
be cited with a violation of the rules. In addition, enforcement is possible
by reviewing construction permits in the affected counties and performing
spot checks at construction sites. The commission plans to use public education
and public awareness as part of the enforcement strategy to ensure that the
requirements of these rules are understood and that they will be enforced.
Lake Jackson commented that they have 22 pieces of non-road equipment and
believe that they would be able to replace most of the equipment to comply
with these rules. TxDOT commented that up to 138 pieces of equipment would
be subject to these rules and that they would comply with these rules.
The commission appreciates Lake Jackson and TxDOT identifying these pieces
of equipment for compliance with these rules.
EPA commented that the commission should provide information regarding
the viability of the alternative means of compliance.
The EPA comments allude to the provision in the rules for the emissions
reduction plan. In addressing the viability of alternative measures that could
be used in such a plan, the commission is developing a guidance document for
this plan. A workshop has already taken place where stakeholders were invited
and were given drafts of the requirement of the emissions reduction plan and
asked for their input and comments. Further workshops will be held and the
commission intends to work with the stakeholders to come up with an emissions
reduction plan guidance document that will be workable and agreeable to everyone.
ARTBA commented that the commission should not over-regulate the construction
industry. They stated that the industry is already heavily regulated by the
EPA emission standards on construction equipment.
The commission disagrees with this characterization of the construction
industry as "heavily regulated." It is true that the EPA has issued emission
standards for categories of non-road engines used by the construction industry.
However, these standards were promulgated well after the federal statutory
deadline and did not require any reductions until 1996, nor were any significant
reductions required until the 2001 - 2006 time frame. The EPA has never regulated
the non-road diesel fuel used in construction equipment, nor has the EPA regulated
the hours which that equipment can be used. Until this year the commission
had not regulated emissions from construction equipment, except incidentally
as part of permitting actions. The commission has historically focused its
regulations on point sources and on-road vehicles. Due to the efforts of state
and federal agencies, these point sources and motor vehicles have become substantially
cleaner over time and, as a result, the emissions from construction activities
have increasingly made up a disproportionate amount of the emissions inventory.
Given the amount of reductions needed to demonstrate attainment for the HGA
SIP, the commission must require substantial reductions from all sectors including
point sources, on-road vehicles, and non- road engines. Therefore, the commission
does not agree that the construction industry is being over- regulated as
part of the HGA SIP.
Three individuals commented about on-road diesels. One individual commented
that the soot emissions coming from diesels cars are ten times higher than
others. Two individuals commented that something should be down about the
black smoke being emitted from diesel trucks. One of these individuals commented
that it is a distraction in traffic, while the other individual commented
that new equipment that is sold should have lower emissions, and existing
equipment should be required to be replaced or upgraded. Both individuals
commented that some sort of device be applied to existing diesel trucks to
reduce emissions.
These commenters suggestions are beyond the scope of this rulemaking because
these rules only affect non-road engines and equipment. However, the commission
is considering for adoption, concurrent with this rulemaking, low-emission
diesel fuel standards which would lower emissions from diesel trucks. Also,
in the near future, new federal standards for on-road, heavy-duty diesel trucks
will begin.
TxDOT suggested that the requirement in the rules that require 25% of the
50 to 100 hp fleet be Tier 2 by December 31, 2004, should be changed to 10%.
They stated that because this equipment does not become available until 2004,
then it may be hard to meet the 25% requirement.
The commission made no change in response to this comment. The commission
believes that the 25% requirement will be achievable, and anticipated that
OEMs will provide sufficient numbers of equipment in response to these rules
because of the market that will be created. The commission also anticipates
that many entities will choose to implement an emissions reduction plan, thus
somewhat lessening the demand for the new equipment. However, when the SIP
mid-course correction occurs in the 2003 to 2004 time frame, the commission
will evaluate whether changes to the rule requirements will need to be made.
Brett & Wolf commented that for purposes of complying with the rules,
a fleet owner or operator should be allowed choose to replace existing diesel-fueled
equipment with units powered by gas turbines and/or fuel cells, and that these
be counted as part of the fleet meeting the Tier 3 diesel standards under
30 TAC §114.472.
The commission believes that if it is feasible for a fleet owner or operator
to replace diesel equipment with gas turbines and/or fuel cells, then they
may do so. If all non-road equipment is converted to use these technologies
then the fleet would not be subject to these rules, because gas turbines and/or
fuel cells are not compression-ignition engines. Also, converting engines
to these technologies is certainly a measure which could be included in an
emissions reduction plan.
Sierra-Houston commented that the under 30 TAC §114.476, records should
be maintained for five years because, this is the length of time the commission
uses for compliance history.
The commission disagrees that records should be maintained for five years.
Because the annual reports will be kept by the commission, more than three
years of recordkeeping for an owner/operator is not deemed necessary. The
commission made no change in response to this comment.
PHA commented that EPA approval of an emissions reduction plan should not
be necessary. They commented that the commission has the requisite authority
to approve the plans and should not require EPA approval. Therefore, PHA requested
that 30 TAC §114.477(b) be revised to delete the phrase "and the EPA"
with regard to plan approval.
The commission disagrees with this comment. Because this plan is part of
a SIP strategy, an EPA review of the emissions reduction plans is prudent
to ensure that the SIP is complete, approvable, and enforceable.
STATUTORY AUTHORITY
The new sections are adopted under TWC, §5.103, which authorizes the
commission to adopt rules necessary to carry out its powers and duties under
the TWC, and under Texas Health and Safety Code, TCAA, §382.017, which
authorizes the commission to adopt rules consistent with the policy and purposes
of the TCAA. The new sections are also adopted under TCAA, §382.011,
which authorizes the commission to control the quality of the state's air; §382.012,
which authorizes the commission to prepare and develop a general, comprehensive
plan for the control of the state's air; §382.019, which authorizes the
commission to adopt rules to control and reduce emissions from engines used
to propel land vehicles; and §382.039, which authorizes the commission
to develop and implement transportation programs and other measures necessary
to demonstrate attainment and protect the public from exposure to hazardous
air contaminants from motor vehicles.
§114.477.Exemptions.
(a)
The following non-road equipment powered by compression-ignition
engines are exempt from §114.472 and §114.476 of this title (relating
to Control Requirements; and Reporting and Recordkeeping Requirements):
(1)
locomotives;
(2)
underground mining equipment;
(3)
marine engines;
(4)
aircraft engines;
(5)
airport ground support equipment;
(6)
equipment used solely for agricultural and/or logging purposes
which includes, but is not limited to, tractors, balers, combines, sprayers,
swathers, and skidders;
(7)
equipment used exclusively for emergency operations to
protect public health and safety or the environment; and
(8)
equipment used exclusively for freezing weather operations.
(b)
Owners or operators who submit an emission reduction plan
by May 31, 2002, which is approved by the executive director and the EPA no
later than May 31, 2003, will be exempt from §114.472 and §114.476
of this title in the counties listed in §114.479 of this title (relating
to Affected Counties) upon implementation of the rules of this division on
December 31, 2004. The executive director may allow plans to be submitted
after May 31, 2002. In any event, a plan must be approved prior to the use
of that plan for compliance with the requirements of this division. In order
to be approved, the plan must demonstrate nitrogen oxide reductions equivalent
to those required by §114.472 of this title and must contain adequate
enforcement provisions. The operators may submit a plan for exemption from
the control requirements of §114.472 of this title, §114.482 of
this title (relating to Control Requirements), or both.
This agency hereby certifies that the adoption has been reviewed
by legal counsel and found to be a valid exercise of the agency's legal authority.
Filed with the Office of the
Secretary of State on December 29, 2000.
TRD-200009079
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Effective date: January 18, 2001
Proposal publication date: August 25, 2000
For further information, please call: (512) 239-0348
30 TAC §§114.482, 114.486, 114.487, 114.489
The Texas Natural Resource Conservation Commission (commission)
adopts new §114.482, Control Requirements; §114.486, Record keeping
Requirements; §114.487, Exemptions; and §114.489, Affected Counties
and Compliance Dates. The commission adopts these revisions to add new Division
9, Houston/Galveston Construction Equipment Operating Restrictions; to Subchapter
I, Non-road Engines; Chapter 114, Control of Air Pollution from Motor Vehicles;
and corresponding revisions to the state implementation plan (SIP). The commission
adopts these new sections in Chapter 114 and revisions to the SIP in order
to control ground-level ozone in the Houston/Galveston (HGA) ozone nonattainment
area. The adopted sections are one element of the control strategy for the
HGA Post-1999 Rate-of-Progress (ROP)/Attainment Demonstration SIP. New §§114.482,
114.486, 114.487, and 114.489 are adopted
with changes
to the proposed text as published in the August 25, 2000 issue of
the
Texas Register
(25
TexReg
8240).
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE ADOPTED RULES
HGA SIP Background and Historical Summary
The HGA ozone nonattainment area is classified as Severe-17 under the Federal
Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401
et seq.), and therefore is required to attain the one-hour ozone standard
of 0.12 parts per million (ppm) by November 15, 2007. In addition, 42 USC, §7502(a)(2),
requires attainment as expeditiously as practicable, and 42 USC, §7511a(d),
requires states to submit ozone attainment demonstration SIPs for severe ozone
nonattainment areas such as HGA. The HGA area, defined by Brazoria, Chambers,
Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has
been working to develop a demonstration of attainment in accordance with 42
USC, §7410. On January 4, 1995, the state submitted the first of its
Post-1996 SIP revisions for HGA.
The January 1995 SIP consisted of urban airshed model (UAM) modeling for
1988 and 1990 base-case episodes, adopted rules to achieve a 9% ROP reduction
in volatile organic compounds (VOC), and a commitment schedule for the remaining
ROP and attainment demonstration elements. At the same time, but in a separate
action, the State of Texas filed for the temporary nitrogen oxides (NO
Around the same time as the 1995 submittal, the EPA policy regarding SIP
elements and time lines went through changes. Two national programs in particular
resulted in changing deadlines and requirements. The first of these programs
was the Ozone Transport Assessment Group. This group grew out of a March 2,
1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and
Radiation, that allowed states to postpone completion of their attainment
demonstrations until an assessment of the role of transported ozone and precursors
had been completed for the eastern half of the nation, including the eastern
portion of Texas. Texas participated in this study, and it has been concluded
that Texas does not significantly contribute to ozone exceedances in the Northeastern
United States. The other major national initiative that has impacted the SIP
planning process is the revisions to the national ambient air quality standard
(NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing
the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996,
concurrent with the proposal of the standards, the EPA proposed an interim
implementation plan (IIP) that it believed would help areas like HGA transition
from the old to the new standard. In an attempt to avoid a significant delay
in planning activities, Texas began to follow this guidance, and readjusted
its modeling and SIP development time lines accordingly. When the new standard
was published, the EPA decided not to publish the IIP, and instead stated
that, for areas currently exceeding the one-hour ozone standard, that standard
would continue to apply until it is attained. The FCAA requires that HGA attain
the standard by November 15, 2007.
The EPA issued revised draft guidance for areas such as HGA that do not
attain the one-hour ozone standard. The commission adopted on May 6, 1998
and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained
the following elements in response to the EPA guidance: UAM modeling based
on emissions projected from a 1993 baseline out to the 2007 attainment date;
an estimate of the level of VOC and NO
x
reductions
necessary to achieve the one-hour ozone standard by 2007; a list of control
strategies that the state could implement to attain the one-hour ozone standard;
a schedule for completing the other required elements of the attainment demonstration;
a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the
EPA believed made the previous version of that SIP unapprovable; and evidence
that all measures and regulations required by Subpart 2 of Title I of the
FCAA to control ozone and its precursors have been adopted and implemented,
or are on an expeditious schedule to be adopted and implemented.
In November 1998, the SIP revision submitted to the EPA in May 1998 became
complete by operation of law. However, the EPA stated that it could not approve
the SIP until specific control strategies were modeled in the attainment demonstration.
The EPA specified a submittal date of November 15, 1999 for this modeling.
In a letter to the EPA dated January 5, 1999, the state committed to model
two strategies showing attainment.
As the HGA modeling protocol evolved, the state eventually selected and
modeled seven basic modeling scenarios. As part of this process, a group of
HGA stakeholders worked closely with commission staff to identify local control
strategies for the modeling. Some of the scenarios for which the stakeholders
requested evaluation included options such as California-type fuel and vehicle
programs as well as an acceleration simulation mode equivalent motor vehicle
inspection and maintenance program. Other scenarios incorporated the estimated
reductions in emissions that were expected to be achieved throughout the modeling
domain as a result of the implementation of several voluntary and mandatory
state-wide programs adopted or planned independently of the SIP. It should
be made clear that the commission did not propose that any of these strategies
be included in the ultimate control strategy submitted to the EPA in 2000.
The need for and effectiveness of any controls which may be implemented outside
the HGA eight-county area will be evaluated on a county-by-county basis.
The SIP revision was adopted by the commission on October 27, 1999, submitted
to the EPA by November 15, 1999, and contained the following elements: photochemical
modeling of potential specific control strategies for attainment of the one-hour
ozone standard in the HGA area by the attainment date of November 15, 2007;
an analysis of seven specific modeling scenarios reflecting various combinations
of federal, state, and local controls in HGA (additional scenarios H1 and
H2 build upon Scenario VIf); identification of the level of reductions of
VOC and NO
x
necessary to attain the one-hour
ozone standard by 2007; a 2007 mobile source budget for transportation conformity;
identification of specific source categories which, if controlled, could result
in sufficient VOC and/or NO
x
reductions to attain
the standard; a schedule committing to submit by April 2000 an enforceable
commitment to conduct a mid-course review; and a schedule committing to submit
modeling and adopted rules in support of the attainment demonstration by December
2000.
The April 19, 2000 SIP revision for HGA contained the following enforceable
commitments by the state: to quantify the shortfall of NO
x
reductions needed for attainment; to list and quantify potential
control measures to meet the shortfall of NO
x
reductions needed for attainment; to adopt the majority of the necessary rules
for the HGA attainment demonstration by December 31, 2000, and to adopt the
rest of the shortfall rules as expeditiously as practical, but no later than
July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform
a mid- course review by May 1, 2004; and to perform modeling of mobile source
emissions using the EPA mobile source emissions model (MOBILE6), to revise
the on-road mobile source budget as needed, and to submit the revised budget
within 24 months of the model's release. In addition, if a conformity analysis
is to be performed between 12 months and 24 months after the MOBILE6 release,
the state will revise the motor vehicle emissions budget (MVEB) so that the
conformity analysis and the SIP MVEB are calculated on the same basis.
In order for the state to have an approvable attainment demonstration,
the EPA has indicated that the state must adopt those strategies modeled in
the November submittal and then adopt sufficient controls to close the remaining
gap in NO
x
emissions. The modeling and other
analysis supporting these rules and the HGA SIP indicate a gap of approximately
91 tons per day (tpd) of NO
x
reductions is necessary
for an approvable attainment demonstration. The expected emissions shift from
these rules are necessary to successfully demonstrate attainment.
The emission reduction requirements included as part of this SIP revision
represent substantial, intensive efforts on the part of stakeholder coalitions
in the HGA area. These coalitions, involving local governmental entities,
elected officials, environmental groups, industry, consultants, and the public,
as well as the commission and the EPA, have worked diligently to identify
and quantify potential control strategy measures for the HGA attainment demonstration.
Local officials from the HGA area have formally submitted a resolution to
the commission, requesting the inclusion of many specific emission reduction
strategies.
This rule adoption is one element of the control strategy for the HGA SIP.
Adoption and implementation of this control strategy is necessary in order
for the HGA nonattainment area to comply with the requirements of the FCAA
and achieve attainment for ozone. Additional elements of the control strategy
for the HGA SIP are being adopted concurrently in this issue of the
The amount of NO
x
reductions required for
the area to attain the ozone NAAQS has been estimated by extensive use of
sophisticated air quality grid modeling, which because of its scientific and
statutory grounding, is the chief policy tool for designing emission reduction
strategies. The FCAA, 42 USC, §7511a(c)(2), requires the use of photochemical
grid modeling for ozone nonattainment areas designated serious, severe, or
extreme. The modeling has been conducted with input from a technical oversight
committee. Commission staff have continued to improve the air quality modeling
technology and refine emission inventory data. Numerous emission control strategies
were considered in developing the modeling. Varying degrees of reductions
from point sources, on- road and non-road mobile sources, and area sources
were analyzed in multiple iterations of modeling, to test the effectiveness
of different NO
x
reductions. The attainment demonstration
modeling and other analysis submitted for public hearing and comment concurrently
with the HGA SIP show that a significant amount of NO
x
reductions practicably achievable are necessary from ozone control
strategies in order for the HGA nonattainment area to achieve the ozone NAAQS
by 2007, including reductions from surrounding counties included in the HGA
consolidated metropolitan statistical area (CMSA).
Additionally, reductions associated from the ozone control strategies that
will be implemented outside the HGA nonattainment area will benefit the HGA
nonattainment area. This is due to the regional nature of air pollution, the
contribution from mobile sources, and the economies of scale and associated
market advantages related to distribution networks for some strategies. At
the time the 1990 FCAA Amendments were enacted, the focus on controlling ozone
pollution was centered on local controls. However, for many years an ever
increasing number of air quality professionals have concluded that ozone is
a regional problem requiring regional strategies in addition to local control
programs. As nonattainment areas across the United States prepared attainment
demonstration SIPs in response to the 1990 FCAA Amendments, several areas
found that modeling attainment was made much more difficult, if not impossible,
due to high ozone and ozone precursor levels entering from the boundaries
of their respective modeling domains, a dynamic commonly referred to as transport.
Recent science indicates that regional approaches may provide improved control
of ozone air pollution.
The current SIP revision contains rules, enforceable commitments, photochemical
modeling analyses, and calculation of the remaining NO
x
required to reach attainment (gap calculation) in support of the
HGA ozone attainment demonstration. In addition, this SIP contains post- 1999
ROP plans for the milestone years 2002 and 2005, and for the attainment year
2007. The SIP also contains enforceable commitments to implement further measures,
if needed, in support of the HGA attainment demonstration, as well as a commitment
to perform and submit a mid-course review.
The HGA ozone nonattainment area will need to ultimately reduce NO
Purpose and Summary of Proposed Rules
The purpose of these rules is to establish a restriction on the use of
construction and industrial equipment (non-road, heavy-duty diesel equipment
rated at 50 horsepower (hp) and greater) as an air pollution control strategy
to delay the emissions of NO
x
, a key ozone precursor,
until after noon in order to limit ozone formation. The non-road mobile source
category is one of the few sources of ozone-forming emissions that is not
currently regulated by state or federal rules. Federal controls such as cleaner-burning
engines and cleaner-diesel fuel have been proposed, but are not scheduled
to be implemented until the 2004 time frame.
The adopted revisions will provide a similar restriction on the use of
construction and industrial equipment as that previously adopted by the commission
for the Dallas/Fort Worth (DFW) ozone nonattainment area, except that the
effective period for the HGA ozone nonattainment area is between the hours
of 6:00 a.m. and noon, from April 1 through October 31. The affected area
includes the following counties within the HGA nonattainment area: Brazoria,
Fort Bend, Galveston, Harris, and Montgomery. The contribution towards the
reduction in ozone levels from restricting the hours of operation of construction
and industrial equipment is an essential component of the control strategy
and is necessary for the HGA ozone nonattainment area to demonstrate attainment
with the ozone NAAQS. However, based on estimated population, estimated population
growth, and estimated emissions developed using EPA-approved methodologies,
the commission believes it is not necessary to include Chambers, Liberty,
and Waller Counties in the adopted rules. This issue is discussed in greater
detail in the ANALYSIS OF TESTIMONY section of this preamble.
The effective date of the amended rules for HGA will be April 1, 2005.
The commission established an effective date in 2005 to allow manufacturers
time to produce and release new cleaner- burning equipment and retrofit technology,
which would enable equipment operators to plan for and implement purchases
of this equipment before rules concerning restrictions on the operation of
construction and industrial equipment become effective.
Equipment Classification
The equipment to which the rules concerning operating restrictions apply
includes all non-road, heavy-duty diesel equipment classified as "construction
equipment" or "industrial equipment," rated at 50 hp and greater, regardless
of how that equipment is being used. "Construction equipment" includes, but
is not limited to, pavers, tampers/rammers, plate compactors, concrete pavers,
rollers, scrapers, paving equipment, surfacing equipment, signal boards/light
plants, trenchers, bore/drill rigs, excavators, concrete/industrial saws,
cement and mortar mixers, cranes, graders, off-highway trucks, crushing/processing
equipment, rough terrain forklifts, rubber tire loaders, rubber tire tractors/dozers,
tractors/loaders/backhoes, crawler tractors/dozers, skid steer loaders, off-highway
tractors, and dumpsters/tenders. "Industrial equipment" includes, but is not
limited to, aerial lifts, forklifts, sweepers/scrubbers, other general industrial
equipment, other material handling equipment, air conditioning/refrigeration
equipment, and terminal tractors. Agriculture equipment, such as tractors,
combines, balers, agricultural mowers, agricultural sprayers, irrigation sets,
and tillers greater than six hp, are not considered to be construction or
industrial equipment, and are therefore not regulated under these rules.
Ozone Formation
Ozone is formed through chemical reactions between natural and man-made
VOC and NO
x
emissions in the presence of sunlight.
The critical time for the mixing (chemical reactions) of NO
x
and VOC is early in the day, and thus, higher ozone levels occur
most frequently on hot summer afternoons. By delaying the hours of operation
of construction and industrial equipment, and delaying the release of NO
This strategy is not dependent on atmospheric conditions to reduce ozone
formation, as such strategies are disfavored by 42 USC, §7423. Instead,
the strategy creates reductions in the amount of NO
x
added to the atmosphere by construction and industrial equipment
during the time of day when those emissions have been shown to contribute
to exceedances of the ozone NAAQS. The use of "time of day" restrictions such
as this for NAAQS compliance strategies was supported by the EPA in their
non-road mobile source rules.
Emissions Reduction Plan
This rule contains a provision that allows operators to submit an emissions
reduction plan by May 31, 2002, which, if approved by the executive director
and the EPA by May 31, 2003, could allow the operation of construction or
industrial equipment between the hours of 6:00 a.m. and noon during the restricted
months. The executive director may allow plans to be submitted after May 31,
2002. In any event, a plan must be approved prior to the use of that plan
for compliance with the requirements of this division. The commission anticipates
that by offering this exemption in the HGA area, equipment manufacturers will
invest in additional emission reduction research for construction and industrial
equipment, and therefore advance the state of the art in emission reduction
technology.
The emissions reduction plan must describe in detail how the operator will
reduce NO
x
emissions no later than April 1, 2005
by an amount equivalent to the total NO
x
reductions
that would have been achieved if the operator had otherwise complied with
the rules. Owners or operators may submit plans to apply for exemption from
either the construction equipment operating restrictions rules, the accelerated
purchase of non-road heavy-duty diesel equipment rules, or from both sets
of rules. The plans must contain emission reductions equivalent to the total
NO
x
reductions that otherwise would have been
required by the rules, and must describe how the operator plans to ensure
compliance with the provisions of the rules. Examples of possible modifications
which may result in emission reductions include using new, cleaner-burning
equipment, replacing existing equipment with cleaner-burning engines, retrofitting
existing equipment with emissions-reducing technology, using emissions-reducing
fuel, changing hours of operation, restricting equipment idling, and participating
in an emissions banking and trading program. For example, an owner or operator
may obtain emission reduction credits (ERCs), mobile emission reduction credits
(MERCs), discrete emission reduction credit (DERCs), or mobile discrete emission
reduction credit (MDERCs) in accordance with this section and 30 TAC Chapter
101 (General Air Rules), §101.29 (Emission Credit Banking and Trading).
Note: in a concurrent rulemaking (rule log number 1998-089-101-AI), the emission
credit banking and trading rules are being moved to Chapter 101, Subchapter
H (Emissions Banking and Trading), Division 1 (Emission Credit Banking and
Trading) and Division 4 (Discrete Emission Credit Banking and Trading).
In order to quantify the NO
x
and VOC emission
reductions and equivalent ozone reductions resulting from the fleet modifications,
the commission will apply the same construction and industrial equipment emission
inventory factors used in the modeling to develop these rules. The commission
is developing a guidance document that will be available by May 31, 2001 to
assist operators in developing their plans. The guidance document will outline
requirements for the emissions reduction plan exemption in detail. A working
draft of the guidance document is currently available. The commission is accepting
comments on it from all interested parties until May 1, 2001, and is holding
workshops for all interested parties to give input into the development of
the document. The commission estimates that these rules will result in an
approximate 7.9 tpd shift of NO
x
emissions from
morning to afternoon, which is equivalent to about 6.7 tpd of NO
x
reductions.
The commission is requiring submission of the plans by May 31, 2002 to
allow sufficient time to review and quantify the collective emission reductions
the plans propose. The executive director and the EPA will complete the reviews
by May 31, 2003, which coincides with the planned mid-course review of all
control measures included in the SIP. After reviewing the plans, the executive
director will determine whether the collective emission reductions proposed
by the plans are equivalent to the NO
x
reductions
that would have been achieved from implementing the underlying rules. The
commission will implement the construction equipment operating restrictions
rules on April 1, 2005 and the accelerated purchase rules on December 31,
2004, as adopted, for operators who did not submit plans or whose plans were
not approved.
The commission has determined that the fiscal implications may be significant
due to the shift in work hours. The restriction in the hours of operation
may require that companies adjust their work schedules to comply with these
restrictions.
Additional Flexibilities
The commission solicited comment on the need for additional flexibility
relating to rule content and implementation which have not been addressed
in this or other concurrent rulemakings. Such flexibility may be available
for both mobile and stationary sources. Additional flexibility may be achieved
through innovative and/or emerging technology which may become available in
the future. Additional sources of funds for incentive programs may become
available to substitute for some of the measures considered here. The commission
received comments from 40 persons and eight individuals regarding these issues.
The comments are addressed in the ANALYSIS OF TESTIMONY section of this preamble.
SECTION BY SECTION DISCUSSION
The adopted new §114.482 establishes time of day operating restrictions
for construction equipment. This new section restricts the operation of any
non-road diesel construction and industrial equipment of 50 hp and above,
between the hours of 6:00 a.m. and noon, from April 1 through October 31.
The description of the time period of the restriction was changed from "Daylight
Savings Time" to "April 1 through October 31" in order to be consistent with
other rules. In response to a comment that the definition of construction
equipment required clarification, the commission added the term "industrial"
in the preamble and rule language in each instance where the types of affected
equipment is mentioned, and also added to the preamble a list of the specific
types of equipment included in the categories "construction and industrial
equipment" that are subject to these rules.
The adopted new §114.486 requires all persons subject to the provisions
of §114.482 to maintain daily records of equipment operated in the affected
counties. The term "industrial" was added to subsection (a) of this section
to clarify the definition of affected equipment. The term "working" was added
to subsection (b) of this section to clarify the time limit to provide records
upon request is to be working days rather than calendar days.
The adopted new §114.487 provides exemptions from the control requirements
of §114.482 and the recordkeeping requirements of §114.486. The
term "industrial" was added to subsection (a) of this section to clarify the
definition of affected equipment. These exemptions include diesel equipment
used exclusively for situations involving emergency operations, and diesel
equipment being used for mixing, transporting, pouring, or processing wet
concrete. For purposes of these rules, emergency equipment is defined as equipment
being used to repair facilities, devices, systems, or infrastructure that
have failed, or are in danger of failing, in order to prevent immediate harm
to public health, safety, or the environment. Therefore, language was added
to subsection (a)(1) to clarify this aspect of the exemption. However, this
exemption does not cover equipment being used for routine maintenance of facilities,
devices, systems, or infrastructure, since such activities are not essential
to prevent greater immediate harm to public health, safety, or the environment.
Subsection (b) contains an exemption that allows operators to submit an
emissions reduction plan by May 31, 2002, which, if approved by the executive
director and the EPA by May 31, 2003 could allow the operation of construction
or industrial equipment between the hours of 6:00 a.m. and noon during the
restricted months. The executive director may allow plans to be submitted
after May 31, 2002. In any event, a plan must be approved prior to the use
of that plan for compliance with the requirements of this division. Each plan
must contain adequate enforcement provisions, and must demonstrate emission
reductions equivalent to the total NO
x
reductions
that would otherwise have been achieved under the rules from which the owner/operator
is applying for exemption: construction equipment operating restrictions in §114.482,
accelerated purchase of Tier 2/Tier 3 diesel equipment in §114.472, or
both sets of rules. The language in subsection (b) was revised to clarify
that the requirement to demonstrate equivalent NO
x
reductions applies to the specific rules from which an exemption is being
requested.
The commission is developing a guidance document that will be available
May 31, 2001 to assist operators in developing their plans. The guidance will
outline requirements for the plan exemption in detail. A working draft of
the guidance is currently available from the commission. A working draft of
the guidance document is currently available. The commission is accepting
comments on it from all interested parties until May 1, 2001, and is holding
workshops for all interested parties to give input into the development of
the document.
The adopted new §114.489 specifies the counties in which these rules
are applicable, and the dates and times the rules are effective. The affected
counties include the counties of Brazoria, Fort Bend, Galveston, Harris, and
Montgomery Counties. Based on estimated population, estimated population growth,
and estimated emissions developed using EPA-approved methodologies, the commission
believes it is not necessary to include Chambers, Liberty, and Waller Counties
in the adopted rules. This issue is discussed in greater detail in the ANALYSIS
OF TESTIMONY section of this preamble. The compliance date for the HGA area
is April 1, 2005. The compliance date was changed to be consistent with the
compliance dates of other rule packages.
FINAL REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the rulemaking in light of the regulatory analysis
requirements of Texas Government Code, §2001.0225, and determined that
the rulemaking meets the definition of a "major environmental rule" as defined
in that statute. "Major environmental rule" means a rule the specific intent
of which is to protect the environment or reduce risks to human health from
environmental exposure and that may adversely affect in a material way the
economy, a sector of the economy, productivity, competition, jobs, the environment,
or the public health and safety of the state or a sector of the state. The
rules are intended to protect the environment and/or reduce risks to human
health from environmental exposure to ozone and, although the commission does
not have cost estimates at this time, construction delays could affect a sector
of the economy in a material way. The adopted rules are intended to implement
an operating-use restriction which would prohibit the operation of heavy-duty
diesel construction and industrial equipment between the hours of 6:00 a.m.
and noon, from April 1 through October 31. These rules are part of a strategy
to reduce the formation of ozone in the HGA nonattainment area by delaying
NO
x
emissions from construction and industrial
equipment until later in the day when optimal conditions for the formation
of ozone no longer exist. The rules were developed to help the HGA ozone nonattainment
area demonstrate attainment of the ozone NAAQS. The rules are one element
of the HGA Post-1999 ROP/Attainment Demonstration SIP.
These adopted rules do not meet any of the four applicability criteria
for requiring a regulatory analysis of "major environmental rule" as defined
in the Texas Government Code. Section 2001.0225 applies only to a major environmental
rule the result of which is to: 1) exceed a standard set by federal law, unless
the rule is specifically required by state law; 2) exceed an express requirement
of state law, unless the rule is specifically required by federal law; 3)
exceed a requirement of a delegation agreement or contract between the state
and an agency or representative of the federal government to implement a state
and federal program; or 4) adopt a rule solely under the general powers of
the agency instead of under a specific state law.
As discussed earlier in this preamble, this rule adoption is one element
of the control strategy for the HGA SIP. Adoption and implementation of this
control strategy is necessary in order for the HGA nonattainment area to comply
with the requirements of the FCAA and achieve attainment for ozone. Additional
elements of the control strategy for the HGA SIP are being adopted concurrently
in this issue of the
Texas Register
, or were
included in the HGA SIP considered by the commission on December 6, 2000,
and planned to be submitted to EPA by December 31, 2000.
These rules do not exceed an express standard set by federal law, since
they implement requirements of the FCAA Provisions of 42 USC, §7410,
require states to adopt a SIP which provides for "implementation, maintenance,
and enforcement" of the primary NAAQS in each air quality control region of
the state. These rules were specifically developed as part of an overall control
strategy to meet the ozone NAAQS set by the EPA under 42 USC, §7409.
While 42 USC, §7410 does not require specific programs, methods, or reductions
in order to meet the standard, state SIPs must include "enforceable emission
limitations and other control measures, means or techniques (including economic
incentives such as fees, marketable permits, and auctions of emissions rights),
as well as schedules and timetables for compliance as may be necessary or
appropriate to meet the applicable requirements of this chapter," (meaning
42 USC, Chapter 85, Air Pollution Prevention and Control). It is true that
42 USC does require some specific measures for SIP purposes, like the inspection
and maintenance program, but those programs are the exception, not the rule,
in the SIP structure of 42 USC. The provisions of 42 USC recognize that states
are in the best position to determine what programs and controls are necessary
or appropriate in order to meet the NAAQS. This flexibility allows states,
affected industry, and the public to collaborate on the best methods for attaining
the NAAQS for the specific regions in the state. Even though 42 USC allows
states to develop their own programs, this flexibility does not relieve a
state from developing a program that meets the requirements of 42 USC, §7410.
In order to avoid federal sanctions, states are not free to ignore the requirements
of 42 USC, §7410 and must develop programs to assure that the nonattainment
areas of the state will be brought into attainment on schedule. Thus, while
specific measures are not prescribed, both a plan and emission reductions
are required to assure that the nonattainment areas of the state will be able
to meet the attainment deadlines set by the FCAA. The EPA has provided the
criteria for both the submission and evaluation of attainment demonstrations
developed by states to comply with the FCAA. This criteria requires states
to provide, in addition to other information, photochemical modeling and an
analysis of specific emission reduction strategies necessary to attain the
NAAQS. The commission's photochemical modeling and other analysis indicate
that substantial emission reductions from both mobile and point source categories
are necessary in order to demonstrate attainment. In this case, this rulemaking
is intended to shift the morning NO
x
emissions,
thereby limiting formation of afternoon peak ozone levels. Specifically, as
noted elsewhere in this rule preamble, the limitation in afternoon peak ozone
production associated with these rules is a necessary element of the attainment
demonstration required by the FCAA.
In addition, 42 USC, §7502(a)(2), requires attainment as expeditiously
as practicable, and 42 USC, §7511a(d), requires states to submit ozone
attainment demonstration SIPs for severe ozone nonattainment areas such as
HGA. By policy, the EPA requires photochemical grid modeling to demonstrate
whether the 42 USC, §7511a(f), NO
x
measures
would contribute to ozone attainment. The commission has performed photochemical
grid modeling which predicts that NO
x
emission
strategies, such as those required by these rules, will result in reductions
in ozone formation in the HGA ozone nonattainment area and help bring HGA
into compliance with the air quality standards established under federal law
as NAAQS for ozone. The 42 USC, §7511a(f), exemption from NO
x
measures for HGA expired on December 31, 1997. The expiration of
the exemption under 42 USC, §7511a(f), was based on the finding that
NO
x
emissions management in HGA is necessary
for attainment of the ozone standard. Therefore, the adopted amendments are
necessary components of and consistent with the ozone attainment demonstration
SIP for HGA, required by 42 USC, §7410.
During the 75th Legislative Session, Senate Bill (SB) 633 amended the Texas
Government Code to require agencies to perform a regulatory impact analysis
(RIA) of certain rules. The intent of SB 633 was to require agencies to conduct
a RIA of extraordinary rules. With the understanding that this requirement
would seldom apply, the commission provided a cost estimate for SB 633 that
concluded "based on an assessment of rules adopted by the agency in the past,
it is not anticipated that the bill will have significant fiscal implications
for the agency due to its limited application." The commission also noted
that the number of rules that would require assessment under the provisions
of the bill was not large. This conclusion was based, in part, on the criteria
set forth in the bill that exempted adopted rules from the full analysis unless
the rule was a major environmental rule that exceeds a federal law. As previously
discussed, 42 USC does not require specific programs, methods, or reductions
in order to meet the NAAQS; thus, states must develop programs for each nonattainment
area to ensure that area will meet the attainment deadlines. Because of the
ongoing need to address nonattainment issues, the commission routinely proposes
and adopts SIP rules. The legislature is presumed to understand this federal
scheme. If each rule adopted for inclusion in the SIP was considered to be
a major environmental rule that exceeds federal law, then every SIP rule would
require the full RIA contemplated by SB 633. This conclusion is inconsistent
with the conclusions reached by the commission in its cost estimate and by
the Legislative Budget Board (LBB) in its fiscal notes. Because the legislature
is presumed to understand the fiscal impacts of the bills it passes, and that
presumption is based on information provided by state agencies and the LBB,
the commission believes that the intent of SB 633 was only to require the
full RIA for rules that are extraordinary in nature. While the SIP rules will
have a broad impact, that impact is no greater than is necessary or appropriate
to meet the requirements of 42 USC.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
It is presumed that "when an agency interpretation is in effect at the time
the legislature amends the laws without making substantial change in the statute,
the legislature is deemed to have accepted the agency's interpretation."
The commission's interpretation of the RIA requirements is also supported
by a change made to the Texas Administrative Procedure Act (APA) by the legislature
in 1999. In an attempt to limit the number of rule challenges based upon APA
requirements, the legislature clarified that state agencies are required to
meet these sections of the APA against the standard of "substantial compliance."
Texas Government Code, §2001.035. The legislature specifically identified
Texas Government Code, §2001.0225 as falling within this standard. The
commission has substantially complied with the requirements of §2001.0225.
Rules adopted for inclusion in the SIP fall within the exception in Texas
Government Code, §2001.0225(a), because they are required by federal
law. The commission performed photochemical grid modeling which predicts that
NO
x
emission shifting, such as that required
by these rules, will result in reductions in ozone formation in the HGA ozone
nonattainment area. This rulemaking does not exceed an express requirement
of state law. This rulemaking is intended to result in reductions in ozone
formation in the HGA ozone nonattainment area and help bring HGA into compliance
with the air quality standards established under federal law. The rulemaking
does not exceed a standard set by federal law, does not exceed an express
requirement of state law (unless specifically required by federal law), and
does not exceed a requirement of a delegation agreement. The rulemaking was
not developed solely under the general powers of the agency, but rather was
specifically developed to meet the federal NAAQS under the authority of the
Texas Clean Air Act (TCAA), §§382.011, 382.012, 382.017, 382.019,
and 382.039.
The commission solicited public comment on the draft RIA and received 14
comments. These comments are addressed in the ANALYSIS OF TESTIMONY section
of this preamble.
TAKINGS IMPACT ASSESSMENT
The commission evaluated this rulemaking action and performed an analysis
of whether the proposed rules are subject to Texas Government Code, Chapter
2007. The following is a summary of that analysis. The specific purpose of
the rulemaking action is to establish a construction and industrial equipment
operating restriction which will delay until after noon NO
x
emissions that lead to high levels of ground-level ozone production.
This rulemaking will act as an air pollution control strategy to reduce ozone
levels necessary for the HGA ozone nonattainment area to be able to demonstrate
attainment with the ozone NAAQS. The affected area includes the following
counties within the HGA nonattainment area: Brazoria, Fort Bend, Galveston,
Harris, and Montgomery. Texas Government Code, §2007.003(b)(13), states
that Chapter 2007 does not apply to an action that: 1) is taken in response
to a real and substantial threat to public health and safety; 2) is designed
to significantly advance the health and safety purpose; and 3) does not impose
a greater burden than is necessary to achieve the health and safety purpose.
Although the rules do not directly prevent a nuisance, prevent an immediate
threat to life or property, or prevent a real and substantial threat to public
health and safety, the rules partially fulfill a federal mandate under the
42 USC, §7410. Specifically, the emissions shift under these rules was
developed in order to meet the ozone NAAQS set by the EPA under the 42 USC, §7409.
In addition, §2007.003(b)(4) provides that Chapter 2007 does not apply
to these adopted rules since it is reasonably taken to fulfill an obligation
mandated by federal law. This action is taken in response to the HGA area
exceeding the NAAQS for ground- level ozone, which adversely affects public
health, primarily through irritation of the lungs. The action significantly
advances the health and safety purpose by shifting ambient NO
x
and reducing peak ozone levels in HGA. Attainment of the ozone standard
will require substantial NO
x
emissions control
and management. Any NO
x
emissions shifting resulting
from the current rulemaking is no greater than what the best scientific research
indicates is necessary to achieve the desired ozone levels. However, this
rulemaking is only one step among many necessary for attaining the ozone standard.
Therefore, the purpose of the rulemaking action is to implement a construction
and industrial equipment time of day operating restriction necessary for the
HGA nonattainment area to meet the ozone NAAQS established under federal law.
The commission has included elsewhere in this preamble its reasoned justification
for adopting this strategy and has explained why it is a necessary component
of the SIP, which is federally mandated. This discussion, as well as the HGA
SIP which is being adopted concurrently, explain in detail that every rule
in the HGA SIP package is necessary and that none of the reductions in those
packages represent more than is necessary to bring the area into attainment
with the NAAQS. For these reasons the rules do not constitute a takings under
Chapter 2007 and do not require additional analysis.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission has determined that the adopted rulemaking relates to an
action or actions subject to the Texas Coastal Management Program (CMP) in
accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural
Resources Code, §§33.201 et seq.), and the commission rules in 30
TAC Chapter 281, Subchapter B, concerning Consistency with the CMP. As required
by 31 TAC §505.11(b)(2) and 30 TAC §281.45(a)(3), relating to actions
and rules subject to the CMP, commission rules governing air pollutant emissions
must be consistent with the applicable goals and policies of the CMP. The
commission has reviewed this rulemaking for consistency with the CMP goals
and policies in accordance with the rules of the Coastal Coordination Council,
and determined that the action is consistent with the applicable CMP goals
and policies. The CMP goal applicable to this rulemaking action is the goal
to protect, preserve, and enhance the diversity, quality, quantity, functions,
and values of coastal natural resource areas (31 TAC §501.12(1)). No
new sources of air contaminants will be authorized and ozone levels will be
reduced as a result of these rules. The CMP policy applicable to this rulemaking
action is the policy that commission rules comply with regulations in 40 Code
of Federal Regulations (CFR), to protect and enhance air quality in the coastal
area (31 TAC §501.14(q)). This rulemaking action complies with 40 CFR
Part 50, National Primary and Secondary Ambient Air Quality Standards, and
40 CFR Part 51, Requirements for Preparation, Adoption, and Submittal Of Implementation
Plans. Therefore, in compliance with 31 TAC §505.22(e), this rulemaking
action is consistent with CMP goals and policies.
The commission solicited comments on the consistency of the proposed rules
with the CMP during the public comment period but received none.
HEARINGS AND COMMENTERS
The commission held public hearings on this proposal at the following locations:
September 18, 2000, in Conroe and Lake Jackson; September 19, 2000 in Houston
(two hearings); September 20, 2000, in Katy and Pasadena; September 21, 2000,
in Beaumont, Amarillo, and Texas City; September 22, 2000, in Dayton, El Paso,
and Arlington; and September 25, 2000, in Austin and Corpus Christi. The comment
period closed at 5:00 p.m. on September 25, 2000. The following persons and
124 individuals provided oral testimony and/or submitted written testimony:
1st Infinity Enterprises, Inc. (Infinity); AAA Asphalt Paving, Inc. (AAA
Asphalt); American Road & Transportation Builders Association (ARTBA);
American Short Line Railroad Association (ASLRRA); Associated Builders &
Contractors of Greater Houston (ABC); Associated General Contractors of America,
Houston Chapter (AGC-Houston); Associated General Contractors of Texas (AGC-Texas);
Association of American Railroads (AAR); Baker Botts, L.L.P. (Baker Botts);
Balfour Beatty (Balfour); Bearden Contracting Company (Bearden); Bell Janitorial
(Bell); BFI Waste Systems of North America, Inc. (BFI); Boring & Tunneling
Company of America, Inc. (BorTunCo); Brazos River Constructors, Inc. (BRC);
Brett & Wolff, L.L.C. (Brett & Wolff); Brown & Brown Insurance
(Brown & Brown); Business Coalition for Clean Air (BCCA); Casa Linda Remodeling,
Inc. (Casa Linda); CCC Group, Inc. (CCC); C.E. Barker, Inc. Underground Construction
(Barker); Centex Homes (Centex); Chambers County Judge Jimmy Sylvia (Chambers
County); Cherry Demolition (Cherry); Chevron Phillips Chemical Company, L.P.
(Chevron); City of La Porte (La Porte); City of Missouri City (Missouri City);
City of Simonton (Simonton); City of Spring Valley (Spring Valley); Clean
Air Partnership (CAP); Clear Lake Area Chamber of Commerce (Clear Lake COC);
Coastal Water Authority (CWA); Conrad Construction Company (Conrad); Contractor
Technology, Inc. (CTI); Dayton Pipe Company (Dayton Pipe); Demar Constructors
(Demar); Dina Industries, Inc. (Dina); Dow Chemical Company (Dow); Drews Custom
Homes (Drews); Earth Material Services, L.L.C. (Earth Material); E.E. Reed
Construction, L.C. (Reed); Ella S.A. Contracting, Inc. (Ella); Emerald Builders
(Emerald); Neal, Gerber, & Eisenberg on behalf of Engine Manufacturers
Association (EMA); Enterprise Products Operating L.P. (Enterprise); Environmental
Defense (ED); Excalibur Construction, Inc. (Excalibur); ExxonMobil Corporation
(ExxonMobil); GR Birdwell Construction, Inc. (GR Birdwell); Grandparents
of East Harris County (GEHC); Greater Houston Builders Association (GHBA);
Harris County Judge Robert Eckels (Harris County); Hassell Construction, Inc.
(Hassell); Higgs Custom Homes (Higgs); Hoar Construction (Hoar); Holmes Homes,
Inc. (Holmes); Houff Energy Corporation (Houff); Benthul & Kean on behalf
of Houston Construction Industry Coalition (HCIC); Houston Contractors Association
(HCA); Houston Metropolitan Planning Organization Transportation Policy Council
(Houston MPO); Independent Electric Contractors, Inc. (IEC); JB Services (JBS);
J & S Contractors, Inc. (J & S); Jim Frankel Custom Homes (Frankel);
Joel A. Trimm Construction Company, Inc. (Trimm); John Holland Construction
Co., Inc. (Holland); Kinder Morgan, Inc. (Kinder Morgan); Kossman Contracting
Company, Inc. (Kossman); Kvaerner; League of Women Voters of Texas (LVW-TX);
Legacy Homes (Legacy); Legal Eagle Contractors Co. (Legal Eagle); Liberty
County Judge Lloyd Kirkhall (Liberty County); Listo Company (Listo); Lyondell-Citgo
Refining, L.P. (Lyondell-Citgo); Manhattan Construction Company (Manhattan);
MB Western Industrial Contracting Company (MB Western); Ms Pamela Berger on
behalf of Houston Mayor Lee Brown (Mayor of Houston); Mesa Mechanical, Inc.
(MMI); Metropolitan Transit Authority (Metro); Mickie Service Company, Inc.
(MSC); RMT, Inc. on behalf of Montgomery County (Montgomery County); Montgomery
County Commissioner, Precinct 1, Mike Metter (Commissioner Metter); Montgomery
County Judge Allen Sadler (Judge Sadler); Montgomery County Soil & Water
Conservation District Number 452 (MCSWCD); Mothers for Clean Air (MCA); Mustang
Tractor & Equipment Company (Mustang Tractor); N & S Construction
Co., L.L.C. (N&S); National Aeronautics and Space Administration (NASA);
National Motorists Association (NMA); National Solid Wastes Management Association
(NSWMA); NBG Constructors, Inc. (NBG); NuHome Design, L.L.C. (NuHome); Nunez
Construction Company, Inc. (Nunez); Paisan Construction Company (Paisan);
Trinity Consultants on behalf of Pasadena Paper, Pasadena Pulp, and Donohue
Industries Inc. (Pasadena/Donohue); Pat Hambrick Construction (Hambrick);
Pate & Pate Enterprises, Inc. (Pate & Pate); Perry Homes; Phillips
66 Company (Phillips 66); PolyTech; Port of Houston Authority (PHA); Protherm
Services Group (Protherm); Public Citizen; Reddico Construction Company (Reddico);
Regional Air Quality Consensus Group on behalf of the Houston-Galveston Area
Council (RAQCG); Reliant Energy, Inc. (REI); State Representative for District
16, Ruben Hope (Representative Hope); State Representative for District 130,
John Culberson (Representative Culberson); Rhodia, Inc. (Rhodia); Rohm and
Haas Chemical Company (Rohm and Haas); S&B Plant Services, Ltd. (S&B);
Sandlin Companies (Sandlin); Sustainable Economic and Environmental Development
Coalition (SEED); State Senator for District 11, Mike Jackson (Senator Jackson);
Sierra Club Houston Regional Group (Sierra - Houston); Slack & Co. Contracting,
Inc. (Slack); Small Business United of Texas (SBU Texas); Solutia; Sprint
Sand & Clay, L.P. (Sprint Sand); Stephen Hann Custom Builders (Hann);
TDIndustries, Inc. (TDIndustries); Jenkins & Gilchrist, L.L.P. on behalf
of TXI Operations, L.P., (TXI); Texas Association of Builders (TAB); Texas
Chemical Council (TCC); Texas Citizens for a Sound Economy (CSE); Texas Department
of Transportation (TxDOT); Texas Forestry Association (TFA) in conjunction
with the Texas Logging Council (TLC); Texas Oil & Gas Association (TxOGA);
Trunkline Gas Company (TGC); U.S. Army Corps of Engineers (USACE); US Home
Corporation (US Home); Union Carbide Corporation (Union Carbide); Union Pacific
Railroad Company (Union Pacific); University of Texas System (UT); Vernor
Material and Equipment (Vernor); and Waste Management (WM).
Commenters generally supporting the proposal included Kinder Morgan, LWV-TX,
Metro, TGC and 15 individuals. Commenters generally opposing the proposal
included Infinity, AAA Asphalt, ARTBA, ABC, AGC-Houston, AGC-Texas, AAR, ASLRRA,
Baker Botts, Balfour, Bearden, Bell, BFI, BorTunCo, BRC, Brett & Wolff,
Brown & Brown, BCCA, Casa Linda, CCC, Barker, Centex, Chambers County,
Cherry, La Porte, Simonton, Spring Valley, CAP, Clear Lake COC, CWA, Conrad,
CTI, Demar, Dina, Dow, Drews, Earth Material, Reed, Ella, Emerald, EMA, ED,
Excalibur, ExxonMobil, GR Birdwell, GEHC, GHBA, Harris County, Hassell, Higgs,
Hoar, Holmes, Houff, HCIC, HCA, IEC, JBS, Frankel, Trimm, Holland, Kossman,
Kvaerner, Legacy, Legal Eagle, Liberty County, Listo, Manhattan, MB Western,
Mayor of Houston, MMI, MSC, Commissioner Metter, Judge Sadler, MCSWCD, MCA,
Mustang Tractor, N&S, NASA, NMA, NSWMA, NBG, NuHome, Nunez, Paisan, Hambrick,
Pate & Pate, Perry Homes, Phillips 66, PolyTech, PHA, Protherm, Public
Citizen, Reddico, RAQCG, REI, Representative Hope, Representative John Culberson,
Rhodia, Rohm and Haas, S&B, Sandlin, SEED, Senator Mike Jackson, Sierra
- Houston, Slack, SBU Texas, Sprint Sand, Hann, TDIndustries, TAB, TCC, CSE,
TxDOT, TFA, TLC, TXI, TxOGA, USACE, US Home, Union Pacific, UT, Vernor, WM,
and 89 individuals.
The following persons and 93 individuals suggested changes to the proposal
as stated in the ANALYSIS OF TESTIMONY section of this preamble: Infinity,
AAA Asphalt, ARTBA, ABC, AGC- Houston, AGC-Texas, AAR, ASLRRA, Baker Botts,
Balfour, Bearden, Bell, BFI, BorTunCo, BRC, Brett & Wolff, Brown &
Brown, BCCA, Casa Linda, CCC, Barker, Centex, Chambers County, Cherry, Chevron,
La Porte, Missouri City, Simonton, Spring Valley, CAP, Clear Lake COC, CWA,
Conrad, CTI, Dayton Pipe, Demar, Dina, Dow, Drews, Earth Material, Reed, Ella,
Emerald, EMA, Enterprise, ED, Excalibur, ExxonMobil, GR Birdwell, GHBA, Harris
County, Hassell, Higgs, Hoar, Holmes, Houff, HCIC, HCA, Houston MPO, IEC,
JBS, J&S, Frankel, Trimm, Holland, Kinder Morgan, Kossman, Kvaerner, Legacy,
Legal Eagle, Liberty County, Listo, Lyondell-Citgo, Manhattan, MB Western,
Mayor of Houston, MMI, MSC, Commissioner Metter, MCSWCD, MCA, Mustang Tractor,
N&S, NASA, NMA, NSWMA, NBG, NuHome, Nunez, Paisan, Pasadena/Donohue, Hambrick,
Pate & Pate, Perry Homes, Phillips 66, PolyTech, PHA, Protherm, Public
Citizen, Reddico, RAQCG, REI, Representative Hope, Rhodia, Montgomery County,
Rohm and Haas, S&B, Sandlin, Sierra - Houston, Slack, SBU Texas, Solutia,
Sprint Sand, Hann, TDIndustries, TAB, TCC, CSE, TxDOT, TFA, TLC, TxOGA, TGC,
Union Carbide, USACE, US Home, Union Pacific, UT, Vernor, and WM.
Harris County supported the comments submitted by Houston MPO, RAQCG, and
CAP. The comments submitted by the BCCA were supported by REI, ExxonMobil,
Chevron, LP, Dow, and Phillips 66. The comments submitted by Texas Industry
Project were supported by Reliant Energy, Inc., ExxonMobil Corporation, Dow
Chemical Company, and Phillips 66 Company. The comments submitted by TCC were
supported by ExxonMobil, Dow, and Phillips 66. ExxonMobil and Phillips 66
also supported the comments submitted TxOGA. The comments submitted by HCA
were supported by Slack and Cherry. The comments submitted by GHBA were supported
by Legal Eagle, NuHome, Legacy, and Perry Homes. The AGC-Houston supported
the comments submitted by HCIC. The Mayor of Houston supported the comments
submitted by Harris County.
ANALYSIS OF TESTIMONY
One individual commented that the public should be informed in simple terms
how much pollution is generated per day and year by heavy construction equipment
between 6 a.m. and noon.
For 1993, which is the base year for modeling for the HGA area, emissions
from heavy-duty diesel construction equipment amounted to 42.4 tpd of NO
One individual asked, "What is the benefit from this rule to Houston's
air quality in terms of percentage improvement?"
The construction equipment operating restrictions rules shift 7.9 tpd of
NO
x
to the afternoon, which is equivalent to
an approximate 6.7 tpd of NO
x
reduction. This
amounts to approximately 1% of the total NO
x
reductions in the HGA area.
One individual asked, "What viable alternatives exist to this provision
(e.g. alternative fuel incentives)?"
The exemption offered by submitting an emissions reduction plan which demonstrates
equivalent reductions offers the possibility for an alternative compliance
method. Also, local stakeholders in the HGA area have expressed an interest
in the creation of programs designed to provide incentives for the achievement
of earlier and/or greater reductions than those reductions anticipated from
currently proposed control measures. Such incentive programs could be effective
technology-forcing tools to obtain substantial innovation and ozone reductions
in the most cost-effective manner possible. Possible components of one such
program applicable to these rules could be the provision of funds on a competitive
basis to entities operating both on- and non-road NO
x
sources to assist in the incremental costs of cleaner equipment (which
could encourage earlier implementation of new technologies, cleaner engines,
and fuels). Other incentive programs could focus on tax incentives, subsidies,
research and development, technological assistance, etc. The commission anticipates
that such programs could be components of the HGA ozone nonattainment SIP,
either as enforceable commitments, as potential future substitute measures
based on per-ton reduction cost and total funding associated with the final
scope of the programs, or as alternative methods of compliance with proposed
control strategies. Any incentive program or other alternative method of compliance
must result in emission reductions equivalent to those contained in these
rules.
Sierra - Houston and one individual commented that there should not be
exceptions to the rule.
The commission disagrees with this comment. The exemptions offered under
these rules will either ensure equivalent emission reductions or will not
result in significant emissions of ozone-forming compounds, so that the ozone
reductions achieved by these rules will not be compromised. The commission
is also committed to offering entities affected by the rules adopted under
the SIP as much flexibility in complying with those rules as possible, while
ensuring that the emission reductions the SIP is intended to achieve are not
compromised. The exemptions allow operators to avoid the operating restriction
while still contributing to the regional clean air goals. Specific justifications
for the existing exemptions are as follows: Equipment, when used for situations
involving emergency operations, including equipment that may have to be used
to repair facilities or devices which have failed in order to prevent greater
immediate harm to the environment or public health, is exempt in order to
ensure protection of public health and the environment. Equipment used while
mixing, transporting, pouring, or processing wet concrete is exempt because
of the temperature sensitivity of these operations during the effective time
period of these rules. In addition, the emissions from wet concrete processing
equipment constitute a very minor contribution to the total emissions from
construction and industrial equipment. Therefore, allowing this particular
equipment to operate during the restricted hours is not expected to significantly
impact peak ozone levels. The emissions reduction plan exemption offered under §114.487(b)
provides flexibility to operators while maintaining ozone reductions equivalent
to those that otherwise would have been achieved under these rules. Equipment
owners/operators that submit a plan demonstrating equivalent emission reductions
may be exempted from §114.482 and §114.486 of the rules. Local stakeholders
in the HGA area have expressed an interest in the creation of programs designed
to provide incentives for the achievement of earlier and/or greater reductions
than anticipated from currently proposed control measures. Such incentive
programs could be effective technology promoting tools to obtain substantial
innovation and ozone reductions in the most cost-effective manner possible.
Possible components of one such program could be the provision of funds on
a competitive basis to entities operating both on- and non-road NO
x
sources to assist in the incremental costs of acquiring cleaner equipment
(which could in turn encourage earlier implementation of new technologies,
cleaner engines, and fuels). Other incentive programs could focus on tax incentives,
subsidies, research and development, technological assistance, etc. The commission
anticipates that such programs could be components of the HGA ozone nonattainment
SIP, as enforceable commitments, as potential future substitute measures based
on per-ton reduction cost and total funding associated with the final scope
of the programs, or as alternative methods of compliance with proposed control
strategies. Any incentive program or other alternative method of compliance
must assure emission reductions equivalent to those that would otherwise have
been achieved by these rules.
AGC-Texas, CCC, Mustang Tractor, and three individuals commented that this
rule unfairly singles out or "targets" the construction industry.
The commission disagrees with this comment. The commission has not singled
out the construction industry. The commission provided in the rule preamble
a list of the equipment covered by these rules, and clarified that the rules
apply to all operators of non-road, heavy-duty diesel construction and industrial
equipment rated at 50 hp and above, with the exception of agricultural users,
regardless of how the equipment is being used. For example, equipment such
as bulldozers used in sanitary landfills, non-road cranes used in demolition,
and rubber tire loaders used in manufacturing and industrial operations are
subject these rules. Construction and industrial equipment were specifically
proposed under these rules because of their significant contribution to of
NO
x
emissions to the HGA area. The commission
is adopting other rules and enforceable commitments for the HGA area to regulate
emissions from other types of non-road diesel equipment, as well as on-road
diesel equipment and vehicles. Reducing emissions from non-road diesel equipment
is also addressed with the accelerated purchase of Tier 2/Tier 3 heavy-duty
diesel equipment rules and the diesel emulsion measure. Emissions from on-road
and non-road diesel equipment are being addressed through the clean diesel
fuel rules which will be effective in 2002 for the 95-county central and eastern
Texas region. Another measure affecting other types of non-road diesel equipment
is the NO
x
reduction systems program. As is evidenced
by the adoption of these measures, the commission is not singling out any
one industry in its efforts to reduce ozone levels to bring the HGA area into
attainment with federal ozone standards.
One individual commented that the number of diesel engines operating non-road
on construction sites in the HGA area is insignificant compared to the number
of diesel engine trucks operating on the road, and that these vehicles are
allowed to operate all hours of the day without limitation.
The commission disagrees with this comment. All diesel-powered vehicles
and equipment registered to be used on-road must use federally certified on-road
diesel fuel. Additionally, on-road diesel vehicles and diesel equipment are
being covered in the low emission diesel fuel rules for the central and eastern
Texas region. Under those rules, all diesel-powered, compression-ignition
engines, both on-road and non-road, will be required to use low emission diesel
when refueling within the 95- county central and eastern Texas region. Other
measures adopted on December 6, 2000 with the HGA SIP revision will also result
in reduced emissions from on-road diesel vehicles. These measures include
diesel emulsion, NO
x
reduction systems, and vehicle
idling restrictions. Therefore, emissions from on-road diesel trucks are already
less polluting than those from non-road diesel equipment, and are less harmful
to human health and the environment.
Two individuals commented that establishing the effective date for this
rule far off into the future adds credence to the conclusion that this measure
is meant to be simply for appearance's sake. Projects that have passed some
critical investment or decision point could be grandfathered while all new
projects could be subject to an earlier effective date.
The commission disagrees with this comment. The commission believes that
setting a 2005 effective date will allow affected persons to have ample time
to plan and prepare for the rules' implementation. This additional time will
also allow manufacturers time to produce new cleaner- burning equipment, fuels,
and retrofit technology, which would enable equipment operators to plan for
and implement purchases of this technology before rules concerning equipment
operating restrictions become effective. The emissions reduction plan offered
under §114.487(b) allows those equipment operators that submit a plan
which demonstrates emission reductions equivalent to the reductions achieved
for their fleet by the construction equipment operating restrictions rules
to operate their affected equipment during the restricted hours. Therefore,
if equipment operators are able to reduce emissions from their equipment by
utilizing such technologies as retrofitting, cleaner-burning equipment, or
cleaner fuels, which the effective date of 2005 would give manufacturers more
time to make more widely available, then they would not be restricted from
operating their equipment, and would not need to alter their schedules to
accommodate the operating restrictions.
Infinity, AAA Asphalt, ARTBA, AGC-Houston, AGC-Texas, Balfour, Bell, Brett &
Wolff, Brown & Brown, BCCA, CCC, Spring Valley, CAP, CWA, Demar, Dow,
Reed, ED, ExxonMobil, Harris County, Hoar, HCIC, Houston MPO, Frankel, Kvaerner,
Legacy, Legal Eagle, Manhattan, Mayor of Houston, MB Western, MMI, MCA, Mustang
Tractor, NuHome, Nunez, Perry Homes, PolyTech, PHA, Protherm, Public Citizen,
RAQCG, REI, Rohm and Haas, S&B, SBU Texas, Hann, TDIndustries, TAB, TxDOT,
US Home, and 19 individuals made the following comments, except as noted.
The commission should eliminate the ban (operating restrictions) and replace
it with an enforceable, market-based incentive program, such as California's
Carl Moyer Program.
Equipment operators should have the option to use newer, more efficient
equipment during all hours, which would provide long-lasting environmental
benefits. Also, it would be more beneficial to require emission-controlled
or electric construction equipment or fleet emission standards rather than
restrict the use of existing equipment.
The commission should replace the ban with other measures that would reduce
pollution from much more significant sources at much less cost to the public,
such as automobiles, cleaner fuels, reducing plant expansions in the area,
limiting the use of restaurant drive-through lanes, shifting school schedules
to mid-September through early June, coordinating traffic lights, and implementing
a four- day work week with ten-hour days.
Replace the ban with a Carl Moyers-type program.
The commission does not believe it should eliminate the operating restrictions
without a quantifiable, and enforceable replacement strategy that will provide
ozone reductions equivalent to those achieved by these rules. The commission
believes the rules should be maintained due to the high level of NO
x
emissions currently generated by non-road equipment. The NO
The commission agrees that economic incentive programs can potentially
be an effective tool for achieving air quality. One such program is the Carl
Moyer program in California. That program appears to be successful in providing
flexibility to the regulated industry while still achieving reductions in
air emissions. The California program is authorized by and funded through
the state legislative process and such legislative approval does not currently
exist for a similar Texas program. The commission will continue to try to
identify economic incentives which it has authority to implement. Because
the commission agrees that market-based incentive programs can be an important
component in encouraging development of new technologies and/or greater or
more cost effective emission reduction strategies, the commission has provided
for the inclusion of economic incentive programs as a component of the HGA
SIP in the future. Note that an exemption offered under §114.487(b) offers
flexibility similar to the Carl Moyer program.
Local stakeholders in the HGA area have expressed an interest in the creation
of programs designed to provide incentives for the achievement of earlier
and/or greater reductions than anticipated from currently proposed control
measures. Such incentive programs may be effective technology promoting tools
to encourage substantial innovation and ozone reductions in the most cost-effective
manner possible. Possible components of one such program could be the provision
of funds on a competitive basis to entities operating both on- and non-road
NO
x
sources to assist in the incremental costs
of acquiring cleaner equipment, which in turn could encourage earlier development
of new technologies, cleaner engines, and fuels. Other incentive programs
could focus on tax incentives, subsidies, research and development, technological
assistance, etc. The commission anticipates that such programs could be components
of the HGA ozone nonattainment SIP, either as enforceable commitments, as
potential future substitute measures based on per-ton reduction cost and total
funding associated with the final scope of the programs, or as alternative
methods of compliance with proposed control strategies.
Allow operator option to use more efficient equipment
at all times.
The commission disagrees with these comments. Even newer, more efficient
equipment produces sufficient emissions to significantly contribute to elevated
ozone levels. The commission does not currently have a method for establishing
or implementing emissions limits for construction or industrial equipment,
and is preempted by federal rules from doing so. However, establishing an
effective compliance date in 2005 will afford the commission additional time
and opportunity to further study and refine the existing equipment and emissions
inventories and modeling to determine the feasibility of implementing emissions
limits for this type of equipment, both new and old, as a way to provide operators
additional flexibility in complying with these rules. The 2005 compliance
date will also allow research and development to continue into alternative
emissions-reducing technologies for non-road, heavy-duty diesel equipment,
such as electrification, which are not currently widely available to the average
equipment owner/operator. In addition, the commission has offered an exemption
under §114.487(b) which will allow equipment owners/operators who do
implement the use of alternate emissions-reducing technologies and/or practices
that reduce emissions beyond those of new equipment, and can demonstrate equivalent
emission reductions from these measures, to operate that equipment during
the restricted hours. This exemption allows equipment operators to take advantage
of existing and emerging alternative emissions-reducing technology which would
allow those operators to use their equipment during the restricted hours if
they are able to demonstrate equivalent emissions reductions. The commission
does not believe it should eliminate the operating restrictions rules because
of the significant contribution that non-road equipment makes to the HGA area
high ozone levels. The NO
x
emissions from non-road
equipment comprise 12% of the HGA area total NO
x
emissions. Because of the significant contribution that non-road equipment
makes to the HGA area ozone levels, it is essential that the construction
equipment operating restrictions rules be implemented along with the other
rules and measures included in this SIP revision in order for the HGA area
to demonstrate attainment with the federal ozone standard.
Replace the ban with lower cost measures directed
at more significant sources.
The commission does not believe it should eliminate the construction equipment
operating restrictions without a quantifiable and enforceable replacement
strategy that demonstrates proven ozone reductions equivalent to those achieved
by these rules. The commission also does not believe it should do away with
the operating restrictions because of the significant contribution that non-road
equipment makes to the HGA area high ozone levels. The NO
x
emissions from non-road equipment comprise 12% of the HGA area's
total NO
x
emissions, a key component in the formation
of ozone. Because of the significant contribution that the equipment affected
by these rules makes to the HGA area ozone levels, it is essential that the
construction equipment operating restrictions rules be implemented along with
other rules and measures included in this SIP revision in order for the HGA
area to demonstrate attainment with the federal ozone standard. The restriction
on hours of operation of non-road, heavy-duty diesel equipment is an essential
component to the overall strategy to reduce peak ozone levels to enable the
HGA area to attain federal ozone standards. Local stakeholders in the HGA
area have expressed an interest in the creation of programs designed to provide
incentives for the achievement of earlier and/or greater reductions than anticipated
from currently proposed control measures. Such incentive programs could be
effective technology- promoting tools to encourage substantial innovation
and ozone reductions in the most cost-effective manner possible. Possible
components of one such program applicable to these rules could be the competitive
provision of funds to entities operating both on- and non-road NO
x
sources to assist in the incremental costs of acquiring cleaner equipment,
which could encourage earlier development of new technologies, cleaner engines,
and fuels. Other incentive programs could focus on tax incentives, subsidies,
research and development, technological assistance, etc. The commission anticipates
that such programs could be components of the HGA ozone nonattainment SIP,
either as enforceable commitments, as potential future substitute measures
based on per-ton reduction cost and total funding associated with the final
scope of the programs, or as alternative methods of compliance with proposed
control strategies. This SIP revision does contain a wide variety of measures
to reduce pollution from the other sources mentioned in this comment. However,
as explained above, the non- road equipment source category is a significant
source of ozone-forming emissions, and therefore must be included in the state's
efforts to reduce ozone.
One individual suggested that the operating restrictions be replaced with
a program resembling a "no drive days" program, which would voluntarily restrict
equipment operation only on certain days of the week, determined by the companies'
geographic location or first letter of the company name.
The commission disagrees with this suggestion because EPA will not approve
a voluntary measure as enforceable or quantifiable, two conditions which all
approvable SIP measures must meet. In addition, the commission does not believe
it should eliminate the construction equipment operating restrictions without
a quantifiable and enforceable replacement strategy that demonstrates provides
ozone reductions equivalent to those achieved by these rules. The commission
does not believe it should eliminate the operating restrictions because of
the significant contribution that non-road equipment makes to the HGA area
high ozone levels. The NO
x
emissions from non-
road equipment comprise 12% of the HGA area's total NO
x
emissions, a key component in the formation of ozone. Because of
the significant contribution that non-road equipment makes to the HGA area
ozone levels, it is necessary that the construction equipment operating restrictions
rules be implemented along with the other rules and measures included in this
SIP revision in order for the HGA area to demonstrate attainment with the
federal ozone standard. The restriction on hours of operation of non-road,
heavy-duty diesel construction and industrial equipment is an essential component
of the overall strategy to reduce peak ozone levels to enable the HGA area
to attain federal ozone standards.
PHA supports the voluntary mobile source emissions program (VMEP) as an
alternative to the operating restrictions. They stated that VMEP offers the
most promise for actual air emission reductions in the HGA area in terms of
new technologies and preemption issues.
The commission disagrees with this comment. The construction equipment
operating restrictions cannot be used as a VMEP, which is a voluntary program,
because the state needs the enforceable emission reductions that the construction
equipment operating restrictions rules provide in order to demonstrate attainment
with the federal ozone standard.
TCC commented that provisions should be made for facilities included in
the area's emissions cap and trade program to be able to include the emissions
from the usage of construction and industrial equipment for maintenance and
turn-arounds in the facilities' allocated cap, to enable facilities to operate
affected equipment during the restricted hours.
The commission disagrees with this comment. Emissions from mobile sources
and stationary sources differ in their potential to form ozone. Emissions
from point sources are emitted higher into the atmosphere, while emissions
from mobile sources are emitted at ground level. Therefore, these two types
of emissions cannot be considered "equivalent" under the cap and trade program,
prohibiting mobile source emissions from being included in a facility's allocations.
However, facilities do have the option of applying for the exemption offered
under §114.487(b), and if approved, would be permitted to operate their
affected equipment during the restricted hours.
TCC also commented that smaller facilities not required to participate
in the cap and trade program should be allowed to either voluntarily opt in
to the cap and trade program to allow them to operate affected equipment during
the restricted hours, or offset emissions from construction and industrial
equipment used in maintenance/turn-around activities with MERCs or DERCs generated
at the facility or purchased from another source in the eight-county nonattainment
area as part of an emissions reduction plan.
Regarding smaller facilities or those facilities not required to participate
in the cap and trade program, it is expected that the commission will add
language to the rules to allow sources exempt from the cap and trade program
to opt in. Regarding MERCs and DERCs, any source that reduces its emissions
voluntarily and meets the requirements of the banking rules will be able to
generate credits. The exemption offered in §114.487(b) gives facilities
the option of offsetting emissions from heavy-duty diesel construction or
industrial equipment by using credits as part of their emissions reduction
plan, provided that the facility meets the requirements of the emissions banking
and trading rules.
TxOGA commented that there will be little chance of oil and gas equipment
operators being able to purchase emissions credits elsewhere because of the
demand for such credits from other types of operations. For all practical
purposes, the §114.487(b) option for an emissions reduction plan will
not be available to these operators.
The commission disagrees that oil and gas operators will have difficulty
purchasing emissions credits. The commission expects that as the demand for
credits, and thus the price for credits, increases, the market will see a
growth of applicants finding ways to generate additional credits. Also under
these rules, more types of mobile sources will be able to generate credits,
thus increasing their availability.
Infinity, AAA Asphalt, ARTBA, ABC, AGC-Houston, AGC-Texas, Balfour, Bearden,
BFI, BorTunCo, BRC, Brown & Brown, BCCA, Casa Linda, CCC, Barker, Centex,
Cherry, Simonton, Conrad, CTI, Demar, Dina, Dow, Drews, Earth Material, Reed,
Ella, Emerald, ED, Excalibur, GRBirdwell, GHBA, Hassell, Higgs, Hoar, Holmes,
HCIC, HCA, IEC, JBS, J&S, Frankel, Trimm, Holland, Kvaerner, Legacy, Legal
Eagle, Listo, Manhattan, MB Western, MMI, Mustang Tractor, N&S, NASA,
NBG, NuHome, Nunez, Paisan, Hambrick, Pate & Pate, Phillips 66, PolyTech,
Protherm, Reddico, Representative Hope, Rohm and Haas, S&B, Sandlin, Slack,
Sprint Sand, Hann, TDIndustries, TAB, TxDOT, TxOGA, Union Pacific, USACE,
US Home, WM, and 29 individuals commented that this rule will create safety
hazards, as much of the work will be done under diminished light conditions,
resulting in reduced safety, increased accident rate, and increased costs
to the clients. Working under lower light conditions with decreased visibility
will also result in lower quality of work and will likely cause errors and
material failures. Use of certain equipment, such as large cranes, cannot
be performed safely at night. Increased fatigue could cause more accidents.
Increased hazards will increase the cost of builders' risk and health insurance.
It is dangerous to work in the heat of the day in Texas. Increased nighttime
road work will result in increased motor vehicle accidents as well as increased
worker fatalities in work zones.
The commission recognizes that these rules may result in increased exposure
to elevated temperatures and increased fatigue and risk for accidents and
injury. However, operators would be expected to take all necessary measures
to protect the health and safety of their employees and educate them about
potential risks. The commission does not have the capability nor authority
to directly regulate worker safety. The ultimate responsibility of the commission
with these rules is to maintain and improve air quality and public health
for all citizens in the HGA area. Regarding the safety concerns of working
in the evening hours with decreased visibility, the change to the time period
between April 1 though October 31 will extend the daylight hours during the
period of the year the rules will be in effect. The increased daylight hours
will minimize any potential risks or quality problems associated with low
visibility. In addition, the commission expects that affected companies will
take necessary measures to ensure the quality of finished products, in order
to retain customers and attract new business. The commission recognizes that
insurance costs may increase due to the increase in activity during the late
afternoon and evening hours, and that affected businesses may have to pass
these costs on to their customers. However, the commission believes that companies
can address customer dissatisfaction over higher costs by explaining that
the cost increases were necessary to enable the company to comply with regulations
that will ultimately improve the customers' air quality and health.
Demar, Reed, Hoar, Kvaerner, Manhattan, MB Western, MMI, NASA, Paisan,
PolyTech, Protherm, Rohm and Haas, TDIndustries, and two individuals commented
that the proposal directly violates Occupational Safety and Health Administration
(OSHA) regulations.
The commission disagrees with this comment to the extent it suggests that
the Commission has jurisdiction over OSHA regulations. While the commission
is charged with protection of human health and the environment, this responsibility
applies to external environmental matters relating to outdoor air quality,
waste and water. The Commission does not have authority over issues of worker
safety, especially with respect to the administration of OSHA regulations.
ARTBA, AGC-Texas, Bearden, BorTunCo, BCCA, Barker, CTI, Earth Material,
Excalibur, HCIC, HCA, NBG, Pate & Pate, Reddico, and five individuals
commented that the impact on the minority community is too great. Both minority
workers and minority-owned businesses will be impacted disparately.
The commission maintains that the rules as adopted will not have a disparate
impact on persons based on race, color, or national origin. The basis for
the rules is protection of human health and the environment, and shifting
the operation of construction and industrial equipment from 6:00 a.m. until
noon during the ozone season is anticipated to provide reductions in the formation
of ozone in the area. Although it is not clear what, if any, legal standard
the commenter allege the commission would violate in adopting the rules, some
state that the rules would "disproportionately impact" minorities. This is
clearly a reference to Title VI of the Civil Rights Act of 1964. In order
for the commission to be shown in violation of Title VI, a disproportionately
negative impact to minorities must be shown; however, any potential negative
impacts that may result from implementation of this rule will be borne equally
by all operators of equipment governed by the rules without any differentiation
by race, color, or national origin. These rules are facially neutral and apply
equally to all operators of the types of equipment affected by these rules.
Infinity, AAA Asphalt, ARTBA, ABC, AGC-Houston, AGC-Texas, AAR, ASLRRA,
Balfour, Bearden, Bell, BorTunCo, BRC, Brown & Brown, BCCA, Casa Linda,
CCC, Barker, Centex, Cherry, La Porte, Simonton, Spring Valley, CAP, Clear
Lake COC, Conrad, CTI, Dayton Pipe, Demar, Dina, Dow, Drews, Earth Material,
Reed, Ella, Emerald, Excalibur, ExxonMobil, GR Birdwell, GEHC, GHBA, Harris
County, Hassell, Higgs, Hoar, Holmes, HCIC, HCA, IEC, JBS, J&S, Frankel,
Trimm, Holland, Kvaerner, Legacy, Legal Eagle, Listo, Manhattan, MB Western,
MMI, Commissioner Metter, MSC, Mustang Trailer, N & S, NBG, NuHome, Nunez,
Paisan, Hambrick, Pate & Pate, Phillips 66, PolyTech, PHA, Protherm, Reddico,
Rohm and Haas, S & B, Sandlin, Slack, Hann, TDIndustries, TAB, CSE, TxDOT,
TxOGA, Union Pacific, UT, US Home, Vernor, WM, and 42 individuals commented
that this rule will have a detrimental impact to the Houston economy and/or
its citizens' and workers' quality of life. Individuals forced to work in
the evenings would no longer be able to spend that time with their families,
and working parents would have limited to no daycare options. This rule will
slow or halt the growth of industry and business, especially small businesses.
The rule will place the region's businesses at a competitive disadvantage.
The construction labor market is already suffering from shortages. Many workers
would be forced to leave the industry or be unemployed to avoid working a
non-traditional work day. The economic impact seems high compared to the value
received.
PHA commented that according to a study conducted by Air Maritime Industry
Strategy Group (AMISG), the operating restrictions will result in $178 million
in additional costs related to Houston and Galveston port operations, either
to the shipper through increased berthing costs or to the ports through lost
business. Thousands of Texas businesses are dependent upon the Houston and
Galveston ports in order to receive critical components necessary for their
operations. Their inability to receive cargo for six hours each day could
force them to shut down operations due to the lack of materials. This could
in turn have a ripple effect through the local and state economy.
Union Pacific commented that they operate loading/unloading equipment throughout
the HGA area at service and repair areas, servicing and fueling centers, classification
and switch yards, and most importantly, at the Port of Houston. If products
cannot be unloaded at intermodal terminals at the port for transport by rail
until noon, schedules will be significantly affected, thereby affecting the
flow of commerce and impacting the economy.
The commission recognizes that compliance with these rules may create short
term losses in productivity, which may result in increased project duration
and costs and negative economic impacts to affected businesses and the communities
in which these businesses operate. However, the commission anticipates that
affected companies and communities will find and make the necessary adjustments
to minimize these impacts, especially considering the far more substantial
economic and quality-of-life impacts that would result from the failure of
the HGA area to attain the federal air quality standards that these rules
are designed to help achieve. The restriction on hours of operation of non-road,
heavy-duty diesel construction and industrial equipment is an essential component
to the overall strategy to reduce peak ozone levels to enable the HGA area
to attain federal ozone standards. Although many of the rules included in
the current SIP attainment strategy may not be easy to implement and may cause
many of the affected entities to have to adjust normal operations and make
certain sacrifices, these rules are of critical importance in the protection
of the environment and human health, which is essential for continued economic
prosperity for all entities affected by the rules. Equipment owners/operators
seeking relief from these rules may choose to apply for an exemption under §114.487(b).
If the application is approved, the owner/operator would be allowed to continue
to operate during the restricted hours. For those businesses that are unable
to qualify for an exemption under the rules, or that choose not to pursue
an exemption, the commission anticipates that they will develop creative solutions
to continue their operations unimpeded. The commission also recognizes that
these rules may cause certain disruptions to the personal and social lives
of affected employees. However, the restriction on hours of operation of non-road,
heavy-duty diesel construction and industrial equipment is an essential component
of the overall strategy to reduce peak ozone levels to enable the HGA area
to attain federal ozone standards. The area's failure to attain these standards
will significantly impact the area economy, and therefore the quality of life
of its citizens and communities. The restriction on hours of equipment operation
prescribed by these rules is based upon well established chemistry and modeling
that demonstrates that shifting morning NO
x
emissions
to later in the day minimizes the likelihood that those emissions will later
form harmful ground level ozone.
The port and rail industries may apply for an exemption under §114.487(b)
and submit an emissions reduction plan, which must demonstrate emission reductions
equivalent to those that would be achieved for the port and rail industries
fleets of affected equipment from implementing the construction equipment
operating restrictions rules. If the port and rail industries are able to
demonstrate equivalent emission reductions from alternate means, these industries
would be able to operate their non-road, heavy-duty diesel construction and
industrial equipment during the restricted hours, thereby reducing concerns
regarding economic and quality of life impacts.
Infinity, ARTBA, AGC-Houston, AGC-Texas, Balfour, Bearden, BorTunCo, Casa
Linda, CCC, Barker, Centex, La Porte, Missouri City, Simonton, Conrad, CTI,
Drews, Earth Material, Ella, Emerald, Excalibur, Hassell, Higgs, Holmes, HCA,
J&S, Frankel, Trimm, Holland, Legacy, Legal Eagle, N&S, NASA, NBG,
NuHome, Paisan, Pate & Pate, Perry Homes, PHA, Sandlin, Slack, Hann, TAB,
TxDOT, US Home, WM, and 12 individuals commented that a significant loss in
construction productivity would result due to loss of morning hours when the
weather is more conducive to higher productivity, and fewer hours in which
to work. This loss in productivity will result in project delays, increasing
project costs.
The commission recognizes that compliance with these rules may create short-term
losses in productivity, which in turn may result in increased project duration
and costs. However, the commission anticipates that affected companies will
find and make the necessary adjustments to minimize these impacts, especially
considering the far more substantial impacts that would result from the failure
of the HGA area to attain federal air quality standards that these rules are
designed to help achieve. The restriction on hours of equipment operation
is an essential component of the overall strategy to reduce peak ozone levels
to enable the HGA area to attain the federal ozone standard. Although many
of the rules included in the current SIP attainment strategy will not be easy
to implement and will cause many of the affected entities to adjust normal
operations and make certain sacrifices, these rules are of critical importance
in the protection of the environment and human health, which is essential
for continued economic prosperity.
TCC commented that many plants use craftsmen for maintenance and turn-arounds
whose schedules are dictated by union contracts. If regulations impose restrictions
on operating equipment from 6 a.m. to noon, some plants could lose as much
as half of their maintenance day.
The commission anticipates that affected facilities will conduct contract
negotiations with the unions to enable union workers to complete their assigned
duties on a schedule that would also allow the facilities to comply with the
equipment operating restriction and maintain operations. The commission anticipates
that the unions will also work with the affected facilities to resolve any
scheduling issues and come to a mutually-agreeable arrangement. Additionally,
facilities that obtain an exemption under §114.487(b) will be able to
continue to operate during the restricted hours, thereby eliminating any need
to modify union contracts.
TxDOT requested that the commission add an exemption for projects currently
under contract and scheduled for completion before the rule implementation
date. Without this exemption, TxDOT would have to modify all existing contracts
to ensure that any projects that are not completed on schedule (by the rule
implementation date) comply with the rule, although only a few projects may
actually extend beyond the implementation date.
The commission does not believe that modifying existing contracts would
be overly burdensome, and therefore does not agree that an exemption should
be added for projects with existing contracts. TxDOT can modify its existing
contracts by adding standard language that would ensure compliance with the
applicable rules if the project extends past the rule implementation date.
BRC, Casa Linda, Barker, Centex, Dayton Pipe, Dow, Drews, Ella, Emerald,
GHBA, Higgs, Holmes, IEC, Sandlin, TAB, TCC, TxDOT, US Home, and three individuals
commented that suppliers would have to alter their delivery schedules to the
evening hours, affecting their economic viability and adding to noise and
pollution in the evening. Deliveries would have to be turned away because
forklifts could not be operated to off-load delivered materials. The disruption
in the flow of goods and services could cost millions of dollars and impede
interstate commerce.
The commission disagrees with these comments. Non-diesel powered forklifts
are common in many warehouses, and are not subject to the operating restrictions
under these rules. Consequently, the commission believes that by 2005 affected
operators will have had the time to plan for the replacement, as necessary,
of their diesel-powered forklifts with non-diesel-powered models. In addition,
the commission anticipates that suppliers of goods and services to companies
affected by these rules may shift their hours of operation or modify their
operations accordingly to retain customers and maintain their businesses.
This will enable affected companies to both comply with the rules and continue
to operate.
Missouri City and three individuals commented that this rule should only
be in effect when weather forecasts call for high ozone, not every day, or
only during the months when ozone is highest, i.e., July and August.
The commission disagrees with this comment. In order to achieve the ozone
reductions necessary to demonstrate attainment with federal standards, the
operating restrictions must be in place from April 1 through October 31. The
risk to human health and the environment would outweigh the benefits gained
by lifting the ban on days when ozone exceedances are less likely to occur,
especially considering the difficulties that would exist with tracking and
enforcement. The commission believes the rules must be in effect during the
entire ozone season, rather than only during certain months, because conditions
can be present at any time during that season for the formation of high levels
of ozone.
One individual commented that this rule should be applicable statewide
and not just in certain areas.
The commission disagrees with this comment. Construction and industrial
equipment inventories and emission inventories do not support the implementation
of these rules on a state-wide basis. These inventories and associated modeling
show that the vast majority of construction and industrial equipment is located
and used in the DFW and HGA metropolitan areas, coinciding with the major
concentrations of population in the state. Therefore, emissions from this
equipment are also concentrated in those areas. In addition, these areas have
air quality problems that are more serious than the rest of the state, primarily
with ozone, the compound that these rules are designed to help reduce. These
existing air quality problems, coupled with the geographic concentration of
equipment usage and emissions, justify implementing rules to control the emissions
of ozone forming compounds from heavy-duty diesel construction and industrial
equipment in the DFW and HGA areas only, rather than statewide. However, these
rules do not preclude other areas considering controls on heavy-duty diesel
construction and industrial equipment from implementing similar locally-regulated
or voluntary programs to achieve similar benefits.
ABC, AGC-Houston, AGC-Texas, Balfour, BFI, BorTunCo, BCCA, Conrad, CTI,
CWA, Dina, Earth Material, ED, Excalibur, HCA, IEC, Trimm, Holland, Listo,
MCA, MCSWCD, NMA, NSWMA, NBG, Pate & Pate, Phillips 66, PHA, Montgomery
County, S&B, Sierra - Houston, TCC, TxDOT, Union Pacific, WM, and 12 individuals
commented that the analytical basis for the rule is flawed and should be re-analyzed.
They also stated that the proposal offers no environmental benefit, the commission
failed to provide adequate scientific and technical justification for the
proposal, and that control measures should reduce emissions, not just shift
those emissions to later in the day. The current SIP guidelines are based
on inaccurate estimates of the non-road vehicle inventory. TxDOT and Sierra
- Houston questioned the accuracy of the construction equipment inventory
used in the modeling for the HGA area SIP.
The commission disagrees with these comments. The commission has worked
extensively with the construction industry and other affected industries in
the HGA area, along with consultants, to ensure that the emissions inventory
and the inventory of affected equipment in the area is as accurate and as
specific to the HGA area as possible. The accuracy of the inventories thereby
maximizes the accuracy of the modeling of the affected industries' contribution
to the air quality problem, as well as the necessary ozone reductions that
this rule is designed to achieve. The commission is required to use a federally-recognized
and approved model for developing data that will be used to demonstrate attainment
with the SIP. The commission used state-of-the-art photochemical methodologies
to develop this rule. The Comprehensive Air Model with Extensions (CAMx) model
that was used is the latest version of the photochemical model recognized
by the EPA for SIP modeling. Also, the Houston Diesel Construction Emissions
project was conducted with the goal of improving upon the emission levels
used previously in the Houston attainment plan. Previous inventories had been
supplied by the EPA in their "Non-Road Equipment and Vehicle Emission Study"
(NEVES, EPA-21A-2001, November 1991). As such, the accepted method to model
years other than the 1990 NEVES data was to apply growth factors from the
Economic Growth Assessment System (EGAS). Technology reduction factors were
then applied to the grown inventories to model new federal emission rules
such as those for diesel engines. Over the last year, however, a new method
of calculating non-road emissions has been developed by the EPA called the
NONROAD model. The NONROAD model will be used to update the attainment modeling
(1993 base case and 2007 future case) for the Houston area because that model
utilizes the best available science with regard to emission factors and treatment
of activity (equipment usage rates) data. The NONROAD model works similar
to the highway emissions model, MOBILE, in that temperatures and fuel qualities
can be modified to better reflect local conditions. The main change to the
NONROAD model input stream was the use of new equipment populations for diesel
construction and industrial equipment. The commission worked with representative
construction operators through independent engineering firms. The general
approach was to define the market share of the representative construction
companies and then upscale the equipment totals based upon estimated total
market share. Local equipment data then had to be adjusted to state equipment
populations using adjustment factors, because NONROAD requires state- wide
totals to perform the county-based calculations. Under contract with the Houston-Galveston
Area Council (HGAC), the Eastern Research Group (ERG) conducted a detailed
survey of construction and industrial equipment populations and activity within
the eight-county HGA ozone nonattainment area. As part of this effort, Starcrest
Consulting facilitated communications with a coalition of local construction
trade organizations and assisted with the development of survey strategies.
Based on the study's findings, input files were generated for use in EPA's
NONROAD emissions model in order to estimate total pollution levels from construction
sources operating in the area. These results serve as an update to the commission's
previous estimates based on EPA's default methodology. Commission staff then
re-ran the NONROAD model using the revised input files to develop a revised
construction emissions inventory for the Houston area. For several reasons
it is believed that the NEVES survey methodology originally used significantly
overestimated equipment populations, and therefore emissions, for the construction
sector in Houston. For example, Houston serves as headquarters for some of
the world's largest construction companies, with thousands of employees dedicated
to engineering and administrative work. However, the employment surrogates
found in the County Business Patterns Report do not distinguish between "office"
and "field" employees. While the number of construction field employees in
a given area may be indicative of overall construction activity, projections
using total "construction employment" in the Houston area may drastically
overestimate overall equipment numbers and activity. For these reasons it
was thought that a "bottom-up" survey of construction and industrial sources
in the area could provide significant improvements to the equipment inventory.
However, previous survey attempts encountered very low response rates, and
ultimately proved unsuccessful. As part of a multi-task contract with HGAC,
ERG agreed to perform a comprehensive survey of all construction and industrial
equipment activity in the eight-county HGA ozone nonattainment area. In order
to improve survey response rates, ERG obtained assistance from a coalition
of several local trade organizations, the Houston Construction Industry Coalition
(HCIC). The HCIC, along with their representative Starcrest Consulting, were
instrumental in identifying key experts for interviews, as well as encouraging
their member companies to actively participate in the survey effort. This
effort provided the commission with a much-improved inventory of construction
and industrial equipment emissions in the Houston area, and resulted in the
revisions incorporated into the Base 6 and Base 6a modeling. Even though the
revised inventory has greatly reduced the uncertainty in construction and
industrial equipment emissions, the commission continually seeks to improve
its inventories. Delaying the rule effective date to 2005 will afford the
commission additional time and opportunity to further address concerns with
all aspects of the existing emissions inventory and modeling and make any
necessary adjustments to the construction and industrial equipment inventory.
AGC-Houston commented that the ramifications of greater NO
x
emissions produced throughout the evening hours are unclear for the
region and bordering areas.
The commission disagrees with this comment. By shifting the emissions into
the evening, the shifted NO
x
will be prevented
from reacting photochemically on the day of the emissions. It is typical and
predictable that NO
x
emissions remaining after
sundown tends to disperse overnight into areas of lower emissions (usually
rural), where they are less likely to lead to high ozone concentrations.
Montgomery County and MCSWCD commented that removing Montgomery County
from the proposed additional air pollution measures will not make any measurable
difference in the Houston ozone problem, and that eliminating Montgomery County
from the construction equipment operating restrictions would result in a difference
of less than 1/50th of 1% of NO
x
, which is equivalent
to less than 1/200th of a part per billion (0.005 ppb) of ozone. One individual
commented that Chambers and Liberty Counties should not be included in this
plan.
The commission continues to believe that in most cases the most effective
method of achieving attainment in the HGA nonattainment area is the implementation
of controls and strategies throughout the nonattainment area. Much of the
HGA control strategy is based on this concept; however, the provisions of
the FCAA recognize that states are in the best position to determine what
programs and controls are necessary or appropriate in order to meet the NAAQS.
This flexibility allows states, affected industry, and the public to collaborate
on the best methods for attaining the NAAQS for the specific areas of the
state. Because of this flexibility, the commission can determine which emission
reduction measures are most needed and where those emission reduction measures
will be the most effective in helping to demonstrate attainment. Based on
estimated population, estimated population growth, and estimated emissions
developed using EPA-approved methodologies, the commission concluded that
the sum of the 2007 projected NO
x
emissions from
non-road, heavy- duty diesel construction and industrial equipment in Chambers,
Liberty, and Waller Counties amounts to just under 2% of the total of those
emissions in the eight-county area. The effect of shifting non- road, heavy-duty
diesel construction and industrial equipment emissions in these three counties
has been modeled, therefore, the commission believes that including these
counties in the adopted rules will have practically no beneficial impact on
peak ozone levels. This is due in part to the fact that these three counties
are primarily rural in nature. The commission believes that non-road, heavy-duty
diesel construction and industrial equipment emissions are more widely dispersed
geographically, and are therefore unlikely to significantly influence the
urban ozone plume. The commission does not, however, believe it is appropriate
to exclude Montgomery County from these rules.
Based on the January 1, 2000 population estimates compiled by the Texas
State Data Center, the population of Chambers County is 26,409; Waller County
is 29,208; and Liberty County is 68,687; for a total of 124,304. The estimated
populations of the remaining five counties in the HGA nonattainment area are:
Brazoria - 236,372; Galveston - 249,898; Fort Bend - 356,555; Harris - 3,275,630;
and Montgomery - 295,263; for a total of 4,413,718. The total estimated population
of the entire HGA nonattainment area is 4,538,022. Thus, the population of
Liberty, Chambers, and Waller Counties combined is only 2.74% of the population
of the entire HGA nonattainment area.
The total NO
x
emissions from all of the HGA
nonattainment counties for non- road, heavy-duty diesel construction and industrial
equipment is 31.54 tpd. The estimated actual NO
x
emissions from non-road, heavy-duty diesel construction and industrial equipment
for Liberty County is 0.22 tpd, for Chambers County is 0.21 tpd, and for Waller
County is 0.19 tpd. The effect of shifting these emissions will result in
equivalent NO
x
emission reductions of 0.05 tpd
in Liberty County, 0.04 tpd in Chambers County, and 0.04 tpd in Waller County,
for a total reduction of 0.13 tpd. These reductions together amount to less
than one-half of 1% of the total of those emissions in the eight-county area.
Based on this data the commission believes it is appropriate not to include
Chambers, Liberty, and Waller Counties in the adopted rules.
The same is not true, however, with respect to Montgomery County, which
the commission believes should be retained. Based on estimated population,
estimated population growth, and estimated emissions developed using EPA-approved
methodologies, the commission concluded that the sum of the 2007 projected
NO
x
emissions from non-road, heavy-duty diesel
construction and industrial equipment in Montgomery County is just over 4%
of the total of those emissions in the eight-county-area (compared to less
than one-half of 1% for Chambers, Liberty, and Waller Counties combined).
The effect of shifting non-road, heavy-duty diesel construction and industrial
equipment emissions in this county has been modeled, therefore the commission
believes that retaining Montgomery County in these rules will have a measurable
and beneficial impact on peak ozone levels. Montgomery County is not primarily
rural in nature, thus non-road, heavy-duty diesel construction and industrial
equipment emissions are not as widely dispersed geographically as in Chambers,
Liberty, and Waller Counties, and therefore are more likely to negatively
influence the urban ozone plume. Based on data compiled by the Texas State
Data Center, Montgomery County is the third largest county in the HGA nonattainment
area with an estimated population of 295,263, or about 6.51% of the total
population of the HGA nonattainment area. The county has more than twice the
population of Chambers, Liberty, and Waller Counties combined. Its NO
AAA Asphalt, ARTBA, AGC-Texas, Balfour, Brown & Brown, CWA, Demar,
Reed, Hassell, Hoar, J&S, Kvaerner, Manhattan, MB Western, MMI, NSWMA,
Phillips 66, PolyTech, PHA, Protherm, Rohm and Haas, S&B, TDIndustries,
TxOGA, USACE, WM, and five individuals commented that this rule would result
in an increased use of electricity and costs for lighting and generators,
which cause pollution, as construction groups are required to work in the
evening to make up for lost morning hours.
The commission disagrees with this comment. Emissions from generators,
classified as "commercial equipment," are not considered to be a significant
contribution to the HGA area ozone levels. While the commission recognizes
that increased emissions may occur at night from artificial lighting, as well
as the compensatory use of additional equipment in the afternoon, those emissions
would occur well past the critical time period during which ozone-forming
emissions combine to eventually form ozone. Therefore, these emissions would
not cause a significant increase in peak ozone levels.
WM, BFI, and NSWMA commented that emissions will likely increase from the
additional waste collection vehicles that will be required to transport waste
within the reduced operating hours and that will be waiting in queue to unload.
BFI commented that emissions will also likely increase from the operation
of additional landfill equipment to accomplish tasks in an abbreviated time
period.
The commission disagrees with these comments. While the commission recognizes
that increased emissions may occur in the afternoon from the compensatory
use of additional equipment in the afternoon, those emissions will occur well
past the critical time period during which ozone-forming emissions combine
to form ozone, and therefore are not expected to cause a significant increase
in peak ozone levels.
PHA commented that implementing the construction ban for port operations
will actually increase NO
x
and ozone in the Houston
Ship Channel rather than reduce it. The port needs to operate 24 hours a day.
The ships would be forced to idle while waiting for the construction and industrial
equipment to perform their needed functions on them. The backlog of idling
ships will add to the NO
x
emissions at the port.
On average, ships require 24 to 56 hours for loading and unloading. Each ship
will therefore sit idle for at least one cycle of the ban. The emissions associated
with the additional idling, and the trickle-down effect on the efficiency
of port operations will outweigh any ozone benefit from shifting loading/unloading
equipment emissions to the afternoon and evening. Not only would the overall
NO
x
emissions at the port and ship channel increase,
but the NO
x
emissions occurring in the morning
hours would also increase. According to a study conducted by the Air Maritime
Industry Strategy Group (AMISG), the inability to load/unload cargo from the
ships will result in an increase in morning NO
x
emissions from trucks and ships. Shore-side power alternatives for vessels
were researched extensively in California but found to be unfeasible.
The commission disagrees with these comments. The port could shift the
hours of operation from the current 7:00 a.m. - 7:00 p.m. schedule to noon
- midnight. This shift in activity would not cause the backlogs and related
increase in emissions from truck idling or vessel dwell times and temporary
berthing associated with trying to maintain the current schedule of operations
under the equipment operating restrictions. If the port is not able to completely
shift operations to after noon, the port could work with the companies representing
the general cargo and container vessels to achieve a workable schedule of
loading/unloading operations that also enables the port to comply with the
equipment operating restrictions. The commission expects that the port can
successfully work with its customers to shift its schedule of operations or
coordinate scheduling to accommodate the operating restrictions, and change
its business practices to ensure a decrease in emissions. The commission acknowledges
that less cargo may be handled at the port because some customers will elect
to take their cargo to other ports outside of the HGA area. The port may be
able to qualify for an exemption under §114.487(b) of the rule. If the
port is able to demonstrate equivalent emission reductions from alternate
means, it would be able to continue its operations during the restricted hours,
thereby reducing concerns regarding economic impacts.
ARTBA, AGC-Houston, AGC-Texas, Bearden, TxDOT, and ten individuals commented
that this measure will add to endless road work and lengthen completion times.
Increased pollution will result from increased congestion.
The commission disagrees with these comments. It is already common practice
to perform high-volume highway construction during off-peak travel hours during
the night and on weekends. Because highway construction often occurs during
off-peak periods, when traffic is lighter, there should be no increase in
traffic congestion. The commission expects that entities performing highway
construction will modify their schedules to minimize any project delays associated
with these rules.
TxDOT, Houston District, stated that they have contractual restrictions
on highway lane closures during peak traffic hours (typically 7:00 a.m. -
9:00 a.m. and 3:00 p.m. - 5:00 p.m.), and some contracts require operations
to cease by sunset. These TxDOT restrictions, coupled with these rule restrictions,
would severely limit the time available to perform road construction.
The commission expects that any contractual conflicts will be resolved
in the common interest of achieving the federal ozone standard. If this standard
is not achieved, the federal government could withhold funding for highway
repairs and construction, which represents a much greater impact on the completion
of road construction projects than the equipment operating restrictions.
AGC-Houston, AGC-Texas, BRC, Centex, Cherry, GHBA, Holland, N&S, Phillips
66, Reddico, TxOGA, and three individuals commented that noise pollution in
residential areas in the evenings would be a problem, and that there are restrictions
against such "after hours" activity in most municipalities.
The commission acknowledges this comment and that equipment operators may
desire to work later hours to compensate for time lost in the early morning.
If this is true, communities may wish to reevaluate their current ordinances
and determine what is best for their community. Because maintaining and improving
air quality, for which these rules are designed, is vital to the health and
welfare of all the citizens in the HGA area, local entities have a vested
interest in taking measures necessary to enable compliance with the rules.
AGC-Texas, BFI, BorTunCo, Casa Linda, Centex, CAP, Conrad, CTI, Dina, Drews,
Earth Material, Ella, Emerald, ED, Excalibur, Harris County, Higgs, Holmes,
HCA, Liberty County, NBG, Pate & Pate, Public Citizen, Sandlin, Sierra
- Houston, Sprint Sand, TAB, US Home, and 14 individuals commented that this
rule will be unenforceable, especially considering the number of employers
using the affected types of equipment in the HGA area. Enforcement would most
likely trickle down to local government, which does not have funding or manpower
to handle this responsibility. One consequence would be no uniformity of enforcement.
The commission disagrees with these comments. Enforcement of the rules
will be achieved in two ways: 1) on-site inspections, and 2) facility records
reviews. The commission anticipates that the primary method of enforcement
will be through records reviews. Additionally, compliance will be determined
by on-site investigations, both routinely scheduled and in response to complaints.
The commission will work with local officials to ensure enforcement of the
SIP and SIP rules. The commission has existing relationships with pollution
control authorities in the City of Houston, Harris County, and Galveston County
for enforcement of other commission rules. The commission will continue to
work closely with local entities in a cooperative effort to maximize its compliance
and enforcement efforts.
AAR, ASLRRA, La Porte, CWA, Dow, Enterprise, Kinder Morgan, Lyondell-Citgo,
Pasadena/Donohue, Phillips 66, PHA, Rhodia, TCC, Union Carbide, Union Pacific,
and two individuals commented that the restrictions would limit businesses'
ability to efficiently perform maintenance operations, and industrial processing
operations, efficiently complete planned unit outages (turn-arounds), and
operate safely. Equipment used for these purposes, such as front-end loaders
and forklifts, should be exempt - specifically, ". . . equipment used in a
manufacturing process as part of normal operations; equipment used in manufacturing,
production, shipping, and receiving activities; equipment used for routine
or scheduled maintenance and/or construction activities at manufacturing facilities;
and equipment used in the moving of materials at a manufacturing plant."
PHA commented that the commission should consider an exemption for port
loading/unloading equipment based on the NO
x
emissions increase (both overall and in the morning hours) and the economic
factors discussed in previous comments. Specifically, PHA requested that §114.487(a)
be revised to add the following clause: "3) Equipment used for cargo handling
(including but not limited to loading and unloading) at a port or marine
terminal facility."
Pasadena/Donohue commented that without the ability to use front-end loaders,
pulping operations at paper mills would not be able to operate during the
restricted hours, as well as recycled paper repulping operations, effectively
shutting down the entire paper recycling mill.
TCC, TxOGA, and Phillips 66 commented that there are many pieces of heavy
equipment at refineries, petrochemical plants, oil production facilities,
pipeline operations and terminals, which are used for maintenance and on-going
production or operation. The rule must clarify for operators that this is
not "construction equipment" and that these should be specifically exempt
from the requirements of §114.482.
The commission acknowledges that the operating restrictions could impact
industrial maintenance and process operations for affected entities throughout
the HGA area. However, the types of diesel equipment used for these purposes
are considered "industrial equipment," and are subject to this rule in the
same way and for the same reasons as construction equipment. Diesel-powered
industrial maintenance and process operation equipment are significant contributors
to high ozone levels in the HGA area. It is therefore important to restrict
the use of this equipment, along with construction equipment, in order to
reduce ozone levels in the HGA area, and to enable the area to attain the
federal ozone standard. The commission does not believe it can exempt this
equipment from the rules and still meet the federal ozone NAAQS. However,
much of the equipment used for industrial maintenance and process operations,
such as forklifts, is already powered by propane engines, or other types of
engines not subject to these rules. Facilities using such alternative equipment
would not be restricted from operating during the restricted hours. Also,
facilities can shift their schedules for routine maintenance and planned unit
outages to accommodate the restriction on equipment operation during the morning
hours. The commission anticipates that facilities which operate continuously
will modify their operations to enable them to comply with the rules while
minimizing any potential disruptions in operations and production. Furthermore,
facilities that qualify for an exemption under §114.487(b) would be able
to continue to operate during the restricted hours. Equipment used at refineries,
petrochemical plants, oil production facilities, pipeline operations and terminals
for maintenance and production or operation is also considered "industrial
equipment," subject to these rules.
Phillips 66 and TxOGA recommended adding the following language in §114.487,
Exemptions: In paragraph (a) add: "3) equipment used exclusively in the exploration,
production, processing, or transportation of crude oil, condensate, or petroleum
products."
TxOGA and Houff commented that it would not be possible to maintain the
levels of oil and gas production, transportation, processing, and manufacture
of refined products to meet the nation's energy needs if the six-hour ban
on startup and operation of non-road diesel equipment is applied to heavy
equipment used "within the process" or for ongoing maintenance of operating
units at these facilities. For example, drilling operations are typically
24-hour-a-day operations, and shutdowns will endanger the wellbore. In addition,
sustaining oil and gas well production requires that wells periodically be
pulled for subsurface equipment repair; such operations need to be performed
when problems occur and cannot be deferred to the winter months without a
loss in production.
The commission acknowledges that the operating restrictions could impact
the oil and gas industry throughout the HGA area. However, because of their
significant contribution to high ozone levels in the HGA area, equipment used
at refineries, petrochemical plants, oil production facilities, pipeline operations,
and terminals for maintenance and production or operation are considered "industrial
equipment," subject to the operating restrictions in the rule. It is necessary
to restrict the use of industrial equipment in order to reduce ozone levels
in the HGA area. The commission expects that oil and gas facilities can schedule
their operations and maintenance to accommodate the restriction on equipment
operation during the morning hours while maintaining adequate production.
The commission anticipates that facilities which operate continuously will
modify their operations to enable them to comply with the rules while minimizing
any potential disruptions in operations and production. Additionally, oil
and gas facilities have the option of applying for an exemption under §114.487(b)
which, if approved, could allow them to continue operations during the restricted
hours.
TXI commented that the 6:00 a.m. to noon ban on the operation of non-road
diesel construction equipment will make it very difficult, if not impossible,
to mine and stockpile sufficient clay for the year-round operation of lightweight
aggregate kilns. Furthermore, the ban would disrupt the loading of product
to customers such as ready-mix concrete companies. The clay can only be mined
during the relatively dry part of the year, which coincides with the time
period of the equipment ban. TXI requested that the commission revise the
proposed equipment operation ban to alleviate hardships that will result to
lightweight aggregate kiln operators and other businesses. TXI also requested
that the commission exempt lightweight aggregate kiln operators from this
rule who can demonstrate that it is necessary to their business activities
to operate the affected equipment during the equipment ban period. Alternatively,
TXI suggested that the commission revise the ban to restrict its applicability
to a narrower range of equipment, thereby lessening the hardship that will
result from the rule.
The commission disagrees with these comments. The commission believes that
the lightweight aggregate kiln industry will be able to shift daily mining
schedules to the afternoon and evening to accommodate the restriction on equipment
operation during the morning hours. The commission anticipates that facilities
will modify their operations to enable them to comply with the rules while
minimizing any potential disruptions in operations and production. Also, facilities
that meet the exemption offered in §114.487(b) would be able to continue
to operate during the restricted hours. The commission recognizes that compliance
with these rules may cause some scheduling and logistical difficulties. However,
the commission expects that affected companies will be able to find and make
the necessary adjustments to minimize these impacts, especially considering
the far more substantial impacts that would result from the failure of the
HGA area to attain federal air quality standards. The restriction on the hours
of operation of construction and industrial equipment is an essential component
of the overall strategy to reduce peak ozone levels in the HGA. Therefore,
the commission does not believe it should exclude the lightweight aggregate
kiln industry from these rules. It is important that all affected industries
that contribute significantly to the elevated ozone levels in the HGA nonattainment
area participate equally in the prevention and reduction of those levels of
ozone. The commission does not believe it should reduce the applicability
of the rules to cover less equipment, because it is essential to include all
construction and industrial equipment in the operating restrictions in order
to achieve adequate ozone reductions to enable the HGA area to attain the
ozone standard. Although some of the rules included in the current SIP attainment
strategy may present some short-term implementation difficulties, and may
even require certain long-term operational adjustments, the commission believes
that these changes are necessary for the protection of human health and the
environment in the HGA area, and are an indispensable part of the effort to
achieve attainment of the federal ozone NAAQS.
WM, NSWMA, and BFI commented that equipment used at solid waste management
facilities should be exempted for the following reasons. 1) Public safety
will be impacted because waste collection vehicles will be forced to pick
up trash in the early evenings when more residents are home and children are
playing on streets in area neighborhoods, and odor and vector problems could
arise from waste accumulating at homes and businesses. 2) Spotters' ability
to identify unacceptable hazardous waste at landfills will be hampered without
the use of spreading equipment. 3) The inability to compact waste during the
busiest hours of operation will significantly decrease the density of waste
and lead to a more rapid consumption of landfill capacity, decreased landfill
stability, increased settling, and increased risk of cap and liner failure.
4) Accumulated waste at the landfill working face or tipping floor will make
it difficult to control odors, windblown trash, birds, rodents, flies, and
potentially the spread of disease. 5) Limited operational capacity at landfills
may result in increased disposal at unregulated facilities. 6) Costs of landfill
development will increase as work would have to occur outside of normal business
hours.
Public safety will be impacted.
The commission disagrees with this comment. These rules do not restrict
the hours of operation of waste collection vehicles, as these are on-road
vehicles, and the rules apply only to non-road equipment. For those facilities
that elect to delay waste collection, the commission expects that they will
take the necessary steps to ensure the safety of customers, such as informing
residents in advance of operational changes by such methods as distributing
notices to customers alerting them to changing hours of operation. The commission
recognizes that facilities may elect to delay collection activities to limit
waste accumulation at landfills, and that solid waste placed at curbside may
sit for longer periods of time before collection. However, the commission
disagrees that a collection delay will necessarily result in additional odor,
litter, and vector problems as collection delays should be minimal. In addition,
waste disposal companies could eliminate problems associated with waste accumulation
at homes and businesses by informing customers of scheduling changes and of
the need to delay setting out their waste for collection. In addition, waste
management facilities have the option of applying for an exemption under §114.487(b)
which, if approved, would allow operations during the restricted hours, thereby
eliminating any need to modify waste collection schedules.
Spotters' inability to identify their waste.
The commission disagrees with this comment. The commission expects that
facilities will develop alternative procedures to ensure the effective identification
of unacceptable wastes. In addition, facilities will have the option of applying
for an exemption under §114.487(b) which, if approved, would allow continued
operations during the restricted hours, thereby reducing any potential problems
associated with the need to use spreading equipment.
Inability to compact waste.
The commission disagrees with this comment. Facilities can minimize many
of these potential problems by making scheduling, design, and operational.
As stated above, facilities will have the option of applying for an exemption
under §114.487(b) which, if approved, would allow continued operations
during the restricted hours, thereby reducing any potential problems associated
with the need to compact waste.
Unacceptable accumulations of waste: orders, vector
attraction
The commission disagrees with this comment. Although waste may be accepted
during the period during which the affected equipment is restricted from operating,
the commission assumes landfill operators will appropriately cover the working
face of their landfills in accordance with all permit and rule requirements,
including those in 30 TAC §330.115, Fire Protection; §330.117, Unloading
of Waste; §330.129, Control of Windblown Waste; §330.125, Air Criteria; §330.126,
Disease and Vector Control; §330.132, Compaction; §330.133, Landfill
Cover; and §330.136, Disposal of Special Wastes. Facilities can minimize
any potential impacts of the rules through design and operational changes,
including additional road and working face lighting, traffic control, segregation
of commercial and private vehicle disposal areas, and use of personnel to
specify dumping locations. The commission expects that waste disposal facilities
will make the necessary scheduling, design, and operational changes to minimize
these potential problems, and avoid permit violations. In addition, facilities
will have the option of applying for an exemption under §114.487(b) which,
if approved, would allow continued operation during the restricted hours,
thereby eliminating any potential problems associated with the need to process
waste during morning collection hours.
Limited operational capacity at landfills.
The commission disagrees with this comment and believes that professional
waste haulers are unlikely to divert their loads to "unregulated facilities."
The commission also does not believe that any potential shift in operations
under these rules will negatively affect the ability of individuals to legally
dispose of their trash at regulated facilities. In addition, facilities will
have the option of applying for an exemption under §114.487(b) which,
if approved, would allow continued operation during the restricted hours,
thereby reducing any potential problems associated with any limited operational
capacity, and illegal disposal at unregulated facilities.
Landfill development costs increase.
The commission disagrees with this comment. The commission expects that
affected facilities will develop strategies to accommodate any shift in business
hours, in order to perform required functions to ensure that the facilities
continue to operate according to permit conditions, while complying with the
restriction on equipment use. In addition, facilities will have the option
of applying for an exemption under §114.487(b) which, if approved, would
allow continued operations during the restricted hours, thereby reducing any
potential problems associated with the costs of landfill development.
NSWMA commented that by not processing the accumulated exposed waste in
a timely manner, there could be an increase in the atmospheric release of
VOCs from the waste, which reduces the air emission benefits from not operating
the equipment.
The commission disagrees with this comment. The operating restrictions,
while offering some shifting of VOC emissions, are primarily a NO
x
-shifting strategy. The commission expects that waste disposal facilities
will make the necessary scheduling, design, and operational changes to minimize
any potential problems from the inability to process waste. In addition, facilities
have the option of applying for the exemption offered under §114.487(b),
and if approved, would be permitted to operate their affected equipment during
the restricted hours, eliminating any potential problems associated with the
inability to process waste.
NSWMA also commented that the time a solid waste facility accepts waste
cannot be extended in most cases because: 1) a facility's permit may limit
the hours of operation to sometime in the afternoon or early evening; and
2) many contracts require the transporter to collect the waste at certain
times, typically between the hours of 7:00 a.m. and 7:00 p.m.
The commission disagrees with comment 1). The commission recognizes that
operators of permitted MSW facilities may find that conditions have changed
such that operating hours and procedures specified in the approved facility
permit (including the Site Operating Plan) need to be revised. Changes to
operating hours of less than one hour beyond the hours specified in the approved
facility permit are considered non-substantive changes and are processed by
the commission MSW Permits Section as Class I permit modifications. Changes
to operating hours of more than one hour beyond the hours specified in the
approved facility permit are considered substantive changes and are processed
by the MSW Permits Section as minor or major amendments, depending upon the
length of extension requested. Changes to operating hours that extend the
hours by more than one hour, but less than two hours are processed by the
MSW Permits Section as minor permit amendments and changes of more than two
hours are processed as major permit amendments. Changes to non-substantive
permit terms and procedures are processed by the commission MSW Permits Section
as Class I modifications under 30 TAC §305.70, Recordkeeping Class I
Modifications, while changes to substantive terms are processed as a minor
or major permit amendment under 30 TAC §305.62, Amendments. The commission
believes that the commission MSW Permits Section has adequate staff and resources
to process amendment or modification requests, that would result from implementation
of these rules, within required processing time frames. Facilities that are
contractually obligated to collect waste between 7:00 a.m. and 7:00 p.m may
need to increase the number of collection vehicles to collect the same volume
of waste in the compressed time period. The commission expects that these
facilities will develop a method to comply with both their contracts and the
equipment operating restrictions.
The commission also disagrees with comment 2). The construction equipment
operating restrictions rules do not directly affect the operational hours
of the waste collection and transporter equipment, as this equipment is on-road,
and the rules only apply to non-road, heavy-duty diesel equipment; therefore,
contracts with waste collectors/transporters would not be impacted. The commission
also notes that because the effective date of these rules is not until 2005,
facilities should have sufficient time to work out any desired changes to
existing, new, or renewed contract terms and conditions. Facilities will have
the option of applying for an exemption under §114.487(b) which, if approved,
would allow continued operations during the restricted hours, thereby reducing
any potential problems associated with permitting or waste collection.
TFA and TLC commented that if the operating restrictions apply to timber
harvesting equipment, harvesting operations would be shut down and serious
restrictions would be placed on the ability to deliver logs from the woods
to the processing mills. Timber harvesting and transportation equipment should
be exempted from these restrictions.
Equipment used to transport harvested timber is not affected by the construction
equipment operating restrictions rules because it is on-road equipment. The
construction equipment operating restrictions rules only apply to non-road,
heavy-duty diesel equipment. Therefore, the operation of transportation equipment
would not be restricted. Equipment such as chainsaws, shredders, fellers,
bunchers, and skidders used in the timber industry are classified as "logging
equipment" and are not subject to the equipment operating restrictions. However,
equipment such as loaders, (including skid steer loaders used with sheer heads)
and bulldozers are classified as "construction equipment" and are subject
to the operating restrictions. It is necessary to restrict the use of construction
and industrial equipment from all affected industry sectors in order to reduce
ozone levels in the HGA. Accordingly, the commission does not believe it should
exclude this type of equipment from these rules. Companies can shift their
operating schedules to accommodate the restriction on equipment operation
during the morning hours. Companies can also modify their operations to minimize
losses in productivity by utilizing equipment not affected by the operating
restrictions to perform necessary operations, or by using artificial lighting
to enable work to continue into the evening hours. Also, companies that obtain
an exemption under §114.487(b) would be able to continue their operations
during the restricted hours. The commission recognizes that compliance with
these rules may cause short-term losses in productivity. However, the commission
anticipates that affected companies will make the necessary adjustments to
minimize these impacts, especially considering the far more substantial impacts
that would result from the failure of the HGA area to attain federal air quality
standards that these rules are designed to help achieve. The restriction on
hours of operation is an essential component of the overall strategy to reduce
peak ozone levels in the HGA Although some of the rules included in the current
SIP attainment strategy may present some short-term implementation difficulties,
and may even require certain long term operational adjustments, the commission
believes that these changes are necessary for the protection of human health
and the environment in the HGA area, and are an indispensable part of the
effort to achieve attainment of the federal ozone NAAQS.
Kossman commented that implementation of the operating restrictions would
have devastating results in their attempts to follow stringent federal guidelines
pertaining to sowing grass seed and planting sod for erosion control, as those
operations must be performed during the first few hours of the day after daybreak.
The commission disagrees with this comment. Equipment used in erosion control
reseeding and sodding operations, such as tractors and hydroseeders, are classified
as "agricultural equipment," and therefore are not subject to the equipment
operating restrictions.
Union Carbide commented that air compressors and portable electric generators
are used to provide fresh air and lighting for confined space work. When work
is not occurring, it is often necessary to keep air compressors working to
keep a fresh air supply going into the confined spaces. Moving the work schedule
to start at noon means that real work may not begin until much later if the
confined space has heated significantly from the sun.
TCC commented that the commission should clarify that, for purposes of
the construction equipment operating restrictions requirements, "utility equipment,"
such as air compressors and welding machines, is not included in "construction
equipment." In addition, the commission should clarify that the rule is not
intended to regulate ship on-board diesel pumps or on-board diesel generators
at chemical plant docks.
One individual commented that his company wouldn't be able to use their
air compressors, water pumps, and welding machines.
The commission concurs with these comments. Equipment items such as air
compressors, welding machines, pumps, and generators are classified as "commercial"
equipment and are not subject to the operating restrictions. This rule applies
only to construction and industrial equipment. The commission has clarified
the types of equipment that are affected by the rules by listing construction
and industrial equipment types in the rule preamble.
The Galveston office of the USACE commented that these rules would have
a devastating impact on deep and shallow draft navigation in the HGA area,
and increase ship channel maintenance dredging costs. The impact is due to
the dredges being precluded from beginning operation until the backlog of
ship traffic that was not able to operate from 6:00 a.m. to noon clears.
The commission disagrees with this comment. The construction equipment
operating restrictions rules do not apply to marine vessels. This rule is
applicable only to non-road, heavy-duty diesel construction and industrial
equipment with engines rated at 50 hp and greater. The marine activity the
individual describes would will not be impacted by this rule, nor will the
activity of the dredging equipment as it relates to the deep draft vessel
operation. However, dredging equipment would still be subject to the rule's
time of day operating restrictions to the extent that equipment qualifies
as "construction" or "industrial equipment."
Chambers County and two individuals commented that diesel restrictions
would affect farmers in the Chambers County area very unfavorably.
The commission disagrees with this comment. The construction equipment
operating restrictions rules do not apply to agricultural equipment. Therefore,
the operating restrictions would not affect farmers unless they were using
construction or industrial equipment which is subject to the rules. In any
event the commission decided, for the reasons previously discussed, not to
include Chambers County in the adopted rules.
Dow, Rhodia, TCC, and Union Carbide commented that equipment used for "emergency
operations" should be exempted, and "emergency" should be redefined in the
rule as "any operation necessary to protect public health, welfare, or the
environment, to ensure continued safe operations." Kinder Morgan requested
that the commission provide an exemption from the operating restrictions for
activities required in emergency situations, including emergency repairs to
gas pipeline facilities. AAR, ASLRRA, and Union Pacific commented that railroad
signal failures need to be fixed immediately or accidents could occur. Safety
concerns could also arise from the railroad's inability to conduct rail/right-of-way
maintenance activities and loading/unloading activities. La Porte commented
that the proposed emergency exemption is vague, and interprets it as being
restricted to life-threatening emergencies. This definition would exclude
maintenance and repair of essential city services and infrastructure, all
of which are regulated by the commission and the EPA. This definition would
prohibit the maintenance and repair of major water leaks, sewer stoppages,
water distribution and wastewater collection systems, wastewater treatment,
street repair and construction, and storm water system maintenance and construction,
some of which would place La Porte in direct violation of permits and regulations
administered by the commission and the EPA. La Porte suggested that the definition
of "emergency" be clarified to include "maintenance and repairs of essential
public infrastructure that protects the health, safety, and welfare of the
public." Enterprise commented that this proposal would jeopardize safety by
hindering a company's ability to respond to upsets and other occurrences that,
while not emergencies in and of themselves, could develop into emergencies
if not promptly addressed.
The commission concurs with these comments, and revised the rule language
of the current exemption in §114.487(a)(1) to include: "equipment being
used for emergency operations to protect public health and safety or the environment,
including equipment being used to repair facilities, devices, systems, or
infrastructure that have failed or are in danger of failing in order to prevent
immediate harm to public health, safety, or the environment." For purposes
of this section, the term "public" includes employees at affected entities.
It should be noted that the exemption in §114.487(a)(1) does not cover
equipment being used for routine maintenance of facilities, devices, systems,
or infrastructure, as those activities are not of an emergency nature and
are not essential to preventing immediate harm to public health, safety, or
the environment. The commission expects that affected entities will adjust
maintenance schedules accordingly or modify operations to accommodate the
operating restrictions, while ensuring the continued safety of the public
and the environment. The commission anticipates that public entities can resolve
any issues regarding conflicts with commission permits or regulations relating
to maintenance of infrastructure. Also, facilities that are able to obtain
an exemption for routine maintenance activities under §114.487(b) will
still be able, during the restricted hours, to continue to perform those activities.
TGC, GPA, and Kinder Morgan fully supported the exemption contained in §114.487(a)(1)
for the protection of public health and safety or the environment. While not
explicitly stated, these entities believe that emergency pipeline repairs
are covered by this exemption due to the public need and necessity of the
transmitted gas. If this assumption is incorrect, these entities respectfully
requested clarification of this point. TxDOT also supported the exemption
for emergency operations, as well as the exemption for wet concrete operations.
The commission agrees in part and disagrees in part with the commenter's
interpretation of the rule with respect to emergency pipeline repairs. Emergency
pipeline repairs are covered under this exemption, not because of the public
need of the transmitted gas, but because of the potential danger to human
health and the environment from a damaged or malfunctioning pipeline. The
commission acknowledges TxDOT's support of the exemption for emergency and
wet concrete operations.
Phillips 66, TxOGA, and one individual commented that the definition of
"construction equipment" needs to be clarified.
The commission agrees with the commenter and wishes to clarify that both
construction and industrial equipment are subject to the rules. The commission
has therefore included the term "industrial" in the preamble and rules in
each instance where the type of equipment affected is mentioned, and has also
added to the preamble a list of the specific types of equipment included in
the categories "construction and industrial equipment" that are subject to
these rules.
One individual commented that the emissions reduction plan exemption should
include a broad number of options, not just related to the heavy equipment
itself.
The commission disagrees that the exemption does not allow for a broad
range of possibilities. The emissions reduction plan exemption does not restrict
what strategies are available to the requestor so long as those strategies
are quantifiable and have demonstrable and constant emission reductions. Equipment
owners/ operators are encouraged to pursue options such as employee trip reduction
measures and other related measures to meet their necessary emission reductions.
Chevron, Phillips 66, PHA, TCC, TxOGA, and one individual commented that
the commission should change the submission date for the emissions reduction
plan to one year prior to the rule compliance date, rather than three years
prior. Phillips 66 and TxOGA commented that the requirement to submit the
emissions reduction plan three years prior to the compliance date is unreasonable,
because the type and amount of equipment in use could change dramatically
in that time frame and significant rework will be required. The requirement
should be shortened to approximately six months (or one year maximum) prior
to the compliance deadline.
The commission disagrees with this comment. The commission is requiring
submission of the emissions reduction plans three years prior to the compliance
date to allow adequate time for review of the plans, both by the commission
and the EPA, and to allow the commission to ensure that the collective emission
reductions achieved by the plans are equivalent to the ozone reductions achieved
by implementation of the rules. This determination will require time-consuming
modeling work, which requires that the plans be submitted as far in advance
of the compliance date as was established in the rules. Regarding the concern
about changes in equipment fleets during the time between submission of the
plans and the compliance date, the calculations in the plans will actually
be based on the owner/operator's best estimate of their fleet as it exists
on the rule implementation date, April 1, 2005. Therefore, any changes that
occur to equipment fleets before that date will not affect the calculations
used to determine an owner/operator's exemption status.
Phillips 66 and TXOGA also commented that the guidance document mentioned
in the proposal should be available 12 months prior to the emissions reduction
plan submission date.
The commission agrees with this comment. The guidance document will be
available May 31, 2001 to aid owners/operators in preparing their emissions
reduction plans. The guidance document will outline requirements for the emissions
reduction plan exemption in detail. A working draft is currently available,
and the commission is accepting comments from all interested parties on the
draft guidance document through May 1, 2001. The commission is also holding
workshops for all interested parties to give input into the development of
the guidance document, to help develop a useful guidance document and a workable
approach for meeting the exemption, and to ensure that the final document
is as useful and helpful as possible in enabling all entities interested in
pursuing an exemption to successfully doing so.
Chevron requested clarification of the criteria and standards that will
be applied in demonstrating to the executive director an alternative, equivalent
emissions reducing measure under §114.487(b). Phillips 66 and TxOGA commented
that the requirements for meeting the alternative emissions reduction plan
exemption need to be outlined within the rule.
The guidance document that will be available May 31, 2001 will outline
requirements for the emissions reduction plan exemption in detail. The commission
does not believe that it is necessary to amend the rule itself, since this
guidance document will thoroughly outline the requirements for an emissions
reduction plan exemption. A working draft is currently available, and the
commission is accepting comments from all interested parties on the draft.
Phillips 66 and TxOGA commented that a quantification of NO
x
reductions are required since the claims of ozone reduction by this
rule are not easily quantified at the equipment or site level.
Commission modelers have calculated the equivalent reductions in NO
TxDOT commented that they appreciate the exemption offered for emissions
offsets, but have concerns about the feasibility of obtaining these reductions.
TxDOT's review of the attainment demonstration and rule packages indicated
that the 6.7 tpd NO
x
equivalent in the construction
shift rule represents a 37% reduction above the Tier 2/Tier 3 and fuel credits.
TxDOT's interpretation of the emission offset exemption is that construction
equipment can continue to operate if NO
x
emissions
can be reduced 37% above the reductions obtained from fuels, diesel emulsions,
and Tier 2/Tier 3 equipment. TxDOT requested clarification on the validity
of those assumptions.
The 37% reduction estimate obtained by TxDOT represents the reductions
expected to be achieved for the fleet of construction and industrial equipment
for the entire HGA area. In order for an individual entity such as TxDOT to
meet the emissions reduction plan exemption, the plan must demonstrate reductions
in NO
x
emissions equivalent to the reductions
that would result from the implementation of either or both rules on their
individual fleet of equipment. Therefore, the reductions required for an individual
fleet should only be a fraction of the 37% of the total reductions. The procedure
for quantifying the required fleet emission reductions under the emissions
reduction plan exemption will be further explained and clarified in the guidance
document that the commission is preparing. The guidance document will be available
on May 31, 2001 to aid owners/operators in preparing their emissions reduction
plans. A working draft is currently available from the commission, and the
commission is accepting comments from all interested parties on the draft
guidance document. The commission is also holding workshops for all interested
parties to give input into the development of the guidance document, to help
develop a useful guidance document and a workable approach for meeting the
exemption, and ensure that the final document is as useful and helpful as
possible in enabling all entities interested in pursuing the exemption in
successfully doing so.
TxOGA commented that most oil and gas operators in the HGA area, simply
because their operations do not generate large volumes of NO
x
, will not have the ability to make offsetting NO
x
emission reductions elsewhere in their operations.
The commission disagrees with this comment. The commission intends to work
cooperatively with all affected entities, large and small, that wish to pursue
the emissions reduction plan exemption, to give them equal ability to utilize
the exemption. The commission is developing a guidance document that will
be available May 31, 2001 to aid owners/operators in preparing their emissions
reduction plans. The guidance document will outline requirements for the emissions
reduction plan exemption in detail. A working draft is currently available
from the commission, and the commission is accepting comments from all interested
parties on the draft guidance document. The commission is also holding workshops
for all interested parties to give input into the development of the guidance
document, to help develop a useful guidance document and a workable approach
for meeting the exemption, and ensure that the final document is as useful
and helpful as possible in enabling all entities interested in pursuing the
exemption in successfully doing so.
Phillips 66 and TxOGA commented that the requirement in §114.487(b)
to demonstrate NO
x
reductions equivalent to those
required by §114.472 as well as §114.482 is not justified, because
an owner/operator's equipment may not be subject to both rules; therefore,
the owner/operator should not be required to demonstrate emission reductions
for a rule to which he or she is not subject. If the requirement is intended
to exempt the equipment from §114.472 as well as §114.482, the rules
need to be revised to do so.
The preamble to the construction equipment operating restrictions rules
for the HGA area clarifies that the emissions reduction plan must describe
in detail how the operator will modify behavior or fleet of equipment to reduce
NO
x
emissions by the implementation date in 2005
by a target amount equivalent to the reductions that would result from the
implementation of either or both rules on their individual fleet of equipment.
Owners or operators may apply for an exemption from either the construction
equipment operating restrictions rules or the accelerated purchase of non-road,
heavy-duty diesel equipment rules, or from both sets of rules. The commission
has also revised §114.487(b) of the rule as follows to clarify that equipment
owners/operators may apply for exemption from either one or both rules: "Operators
that submit an emissions reduction plan by May 31, 2002, which is approved
by the executive director and the EPA no later than May 31, 2003, will be
exempt from operating hour restrictions upon implementation of these rules
in 2005, and will be permitted to operate during the restricted hours. The
executive director may allow plans to be submitted after May 31, 2002. In
any event, a plan must be approved prior to the use of that plan for compliance
with the requirements of this division. In order to be approved, the plan
must demonstrate NO
x
reductions equivalent to
those which would otherwise have been required under the rules, and must also
contain adequate enforcement provisions. The operators may submit a plan for
exemption from the control requirements of §114.472 of this title (relating
to Control Requirements), §114.482 of this title, or both."
PHA commented that EPA approval of an emissions reduction plan should not
be necessary. The commission has the requisite authority to approve the plans
and should not require EPA approval. Therefore, PHA requested that §114.487(b)
be revised to delete the phrase "and the EPA" with regard to approval of the
plans.
The commission disagrees with this comment. The EPA review of the emissions
reduction plans is required to ensure that the SIP is complete, approvable,
and enforceable.
Dow and TCC suggested that the commission delete the requirement for maintaining
daily operating records including equipment start and end times, as this requirement
is overly burdensome with no environmental benefit. The commission should
consider alternate measures to document compliance such as requiring operator
training, or posting of allowable usage on the equipment.
The commission disagrees with this comment. The information needed for
the operating records can be easily recorded and assembled. Additionally,
the records retention requirement should not be overly burdensome. In addition,
companies that obtain an exemption under §114.487(b) will need to maintain
records to demonstrate compliance with the terms of the exemption. The name
of the equipment operator is required because it gives the agency with jurisdiction
to review the records the necessary witness link to verify the authenticity
of the records during a records review. The commission believes it is necessary
to require the recording of the hours of operation of each piece of equipment
to enable the air pollution program with enforcement jurisdiction the ability
to determine a company's compliance with the rules. The commission expects
that affected entities will develop procedures suitable to their specific
operations that will make this recordkeeping as workable as possible.
TCC commented that the commission should revise §114.486(b) as follows:
". . . any records required to be maintained in accordance with this section
within 5
working
days of a written request
. . .." The TCC stated that companies should be given five working days to
complete a request.
The commission agrees with this comment, and has revised the rule to incorporate
the suggested change.
TGC commented that the commission should allow exemptions on a case-by-case
basis for those sources that conduct the majority of their ozone-precursor
forming operations outside of the ozone season. These primarily "winter-operated"
facilities could only be allowed to operate during the restricted period by
purchasing allowance credits from other sources.
The commission disagrees with this comment. The construction equipment
operating restrictions rules do not restrict the operation of heavy-duty diesel
construction and industrial equipment from November through March. Although
certain facilities conduct the bulk of their business operations during the
months outside of the "ozone season," some of their operations are nonetheless
conducted during the ozone season months. These operations, to the extent
they involve non-road, heavy-duty diesel construction or industrial equipment,
still generate ozone-forming NO
x
emissions. The
commission cannot, therefore, use the TGC argument as a valid basis for exempting
their construction and industrial equipment operations. However, TGC has the
option of applying for an exemption under §114.487(b) which, if approved,
would allow operations during the restricted hours of the "ozone season."
TxOGA commented that the rule should allow flexibility such that heavy
equipment usage for actual "construction of new facilities" could be included
in the new source review planning for the facility during permitting. Facilities
could opt to construct during non-ozone season periods or offset the required
emission reductions for the construction period by using DERCs to utilize
a proposed alternative reduction at the plant site, either via curtailment
of a source or reduction within the heavy equipment inventory at the site.
This rule does not restrict the operation of heavy-duty diesel construction
and industrial equipment from November through March. Furthermore, under §114.487(b),
a facility could be able to use DERCs as an alternate strategy for an emissions
reduction plan. If the facility's plan was approved, it would be able to continue
its operations during the restricted hours of 6:00 a.m to noon.
Solutia commented that the commission should allow hourly NO
x
emission reductions from combustion unit shutdowns (for maintenance
turnarounds) to offset the hourly NO
x
emissions
resulting from the operation of construction equipment during the proposed
restriction period.
The commission disagrees with this comment. The commission cannot allow
credits generated from stationary point sources to be used to offset emissions
from mobile sources, as the emissions from these two sources differ in their
potential to form ozone. Emissions from point sources are emitted higher into
the atmosphere, while emissions from mobile sources are emitted at ground
level. Therefore, these two types of emissions cannot be considered "equivalent"
for purposes of banking, trading, or offsetting. However, facilities do have
the option of applying for an exemption under §114.487(b) which, if approved,
would allow continued operations during the restricted hours.
ARTBA, AGC-Texas, BFI, BCCA, ExxonMobil, GRBirdwell, HCIC, Kinder Morgan,
Listo, PHA, SBU Texas, Union Pacific, WM, and two individuals commented that
the commission proposed the draft SIP without a complete analysis and consideration
of its economic feasibility and impacts. The plan lacks the required RIA,
and was proposed without adequate notice, an adequate takings impact assessment,
and an adequate small and micro-business assessment. The commission also failed
to request a local employment impact statement from the Texas Workforce Commission.
The proposed rule and the rulemaking process is procedurally defective because
the commission erroneously concluded that adoption of the workday shift does
not require an RIA. This conclusion is erroneous because the workday shift
exceeds express requirements of state law, is not specifically required by
federal law, and is adopted solely under the general powers of the agency.
The workday shift is not a requirement of federal law because, as the commission
acknowledges in the preamble (25 TexReg 8244) to the rules, the FCAA specifically
defers to states in selection of measures to demonstrate attainment which
is what the federal law does require. The workday shift is a measure that
is the choice of the commission and is in no sense a requirement of federal
law. There being no specific authority for the workday shift under state law,
its only possible statutory basis is the commission's general powers. Because
none of the exceptions apply, the commission is required to perform a RIA
incident to the adoption of a major environmental rule in accordance with
Texas Government Code, 2001.0225. The commission concedes that the workday
shift is such a rule (25 TexReg 8244). Moreover, the commission was required
to incorporate a draft impact analysis into the notice of the proposed rule.
The commission devotes a single conclusory paragraph (25 TexReg 8243) to the
potential impacts. This paragraph has limited cost figures that are attributed
to the TxDOT and an unsupported estimate of an increment cost associated with
the rule. The paragraph does not substantively address the requirements of §2001.025(c).
The proposed rulemaking is thus procedurally defective. The commission failed
to make the required initial determination of whether the rule has the potential
to affect a local economy before proposing the rule for adoption, apparently
ignoring that there is a great potential for the rules to adversely affect
the local economy. BCCA commented that none of the plan's Small and Micro-Business
Assessments applied the mandated cost comparison standards.
Regulatory Impact Analysis
The Texas Government Code, §2001.0225 applies to a major environmental
rule adopted by a state agency, the result of which is to: 1) exceed a standard
set by federal law, unless the rule is specifically required by state law;
2) exceed an express requirement of state law, unless the rule is specifically
required by federal law; 3) exceed a requirement of a delegation agreement
or contract between the state and an agency or representative of the federal
government to implement a state and federal program; or 4) adopt a rule solely
under the general powers of the agency instead of under a specific state law.
This rulemaking action does not meet any of these four applicability requirements,
and is adopted in substantial compliance with the RIA requirements. Texas
Government Code, §2001.035. These rules do not exceed an express standard
set by federal law because the construction equipment operating restrictions
are specifically developed to meet the ozone NAAQS set by the EPA under 42
USC, §7409. Title 42 USC, §7410 requires states to adopt a SIP which
provides for "implementation, maintenance, and enforcement" of the primary
NAAQS in each air quality control region of the state. While 42 USC, §7410
does not specifically prescribe programs, methods, or reductions to meet the
federal standard, state SIPs must include "enforceable emission limitations
and other control measures, means or techniques (including economic incentives
such as fees, marketable permits, and auctions of emissions rights), as well
as schedules and timetables for compliance as may be necessary or appropriate
to meet the applicable requirements of this chapter" (meaning 42 USC, Chapter
85, Air Pollution Prevention and Control). The FCAA does require some specific
measures for SIP purposes, such as an inspection and maintenance program,
but those programs are the exception, not the rule, in the federal SIP structure.
The provisions of the FCAA recognize that states are in the best position
to determine what programs and controls are necessary or appropriate in order
to meet the NAAQS. This flexibility allows states, affected industry, and
the public, to collaborate on the best methods for attaining the NAAQS for
the specific regions in the state. In order to avoid federal sanctions, states
must develop programs to assure that the nonattainment areas of the state
will be brought into attainment on schedule. Thus, while specific measures
are not prescribed, both a plan and emission reductions are required to assure
that the nonattainment areas of the state will be able to meet the attainment
deadlines set by the FCAA. The EPA has provided the criteria for both the
submission and evaluation of attainment demonstrations developed by states
to comply with the FCAA. This criteria requires states to provide, in addition
to other information, photochemical modeling and an analysis of specific emission
strategies necessary to attain the NAAQS. The commissions photochemical modeling
and other analysis indicate that substantial emission reductions from both
mobile and point source categories are necessary in order to demonstrate attainment.
In this case, this rulemaking is intended to shift the morning NO
x
emissions thereby limiting the formation of after noon peak ozone
levels Specifically, as noted elsewhere in this rule preamble, the limitation
in after noon peak ozone production associated with these rules is a necessary
element of the attainment demonstration required by the FCAA.
During the 75th Legislative Session, Senate Bill (SB) 633 amended the Texas
Government Code to require agencies to perform a RIA of certain rules. The
intent of SB 633 was to require agencies to conduct an RIA of major environmental
rules that will have a material adverse impact, and that will exceed a requirement
of state law, federal law, or a delegated federal program, or are adopted
solely under the general powers of the agency. The commission provided a cost
estimate for SB 633 that concluded "based on an assessment of rules adopted
by the agency in the past, it is not anticipated that the bill will have significant
fiscal implications for the agency due to its limited application." The commission
also noted that the number of rules that would require assessment under the
provisions of the bill was not large. Because of the ongoing need to address
nonattainment demonstrations required by federal law, the commission routinely
proposes and adopts SIP rules. If each rule proposed for inclusion in the
SIP was incorrectly considered as exceeding federal law, every SIP rule would
require the full RIA contemplated by SB 633. This result would be inconsistent
with the cost estimates and fiscal notes prepared by the commission and by
the Legislative Budget Board (LLB). Since the legislature is presumed to understand
the fiscal impacts of the bills it passes, and that presumption is based on
information provided by state agencies and the LBB, the commission believes
that the intent of SB 633 was only to require the full RIA for rules that
meet the requirements under §2001.0225(a). While the SIP rules will have
a broad impact, that impact is no greater than is necessary or appropriate
to meet the requirements of the FCAA. In other words, the proposed rules are
intended to meet federal and state law, and does not go above and beyond what
is required to meet federal or state statutes.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
It is presumed that "when an agency interpretation is in effect at the time
the legislature amends the laws without making substantial change in the statute,
the legislature is deemed to have accepted the agency's interpretation."
The commission's interpretation of the RIA requirements is also supported
by a change made to the APA by the legislature in 1999. In an attempt to limit
the number of rule challenges based upon APA requirements, the legislature
clarified that state agencies are required to meet these sections of the APA
against the standard of "substantial compliance." Texas Government Code, §2001.035.
The legislature specifically identified §2001.0225 as falling within
this standard. The commission has substantially complied with the requirements
of §2001.0225.
Rules adopted for inclusion in the SIP fall within the exception in Texas
Government Code, §2001.0225(a), because they are required by federal
law. The commission performed photochemical grid modeling which predicts that
NO
x
emission shifting, such as that required
by these rules, will result in reductions in ozone formation in the HGA ozone
nonattainment area. This rulemaking does not exceed an express requirement
of state law. This rulemaking is intended to result in reductions in ozone
formation in the HGA ozone nonattainment area and help bring HGA into compliance
with the air quality standards established under federal law. The rulemaking
does not exceed a standard set by federal law, does not exceed an express
requirement of state law (unless specifically required by federal law), and
does not exceed a requirement of a delegation agreement. The rulemaking was
not developed solely under the general powers of the agency, but rather was
specifically developed to meet the federal NAAQS under the authority of the
Texas Clean Air Act (TCAA), §§382.011, 382.012, 382.017, 382.019,
and 382.039.
Takings Impact Assessment
The primary reason the commission determined that these rules did not constitute
a takings under Texas Government Code, Chapter 2007 is that they will not
burden private real property. These rules apply to non-road equipment which
is not real property or an appurtenance thereto.
In its analysis, the commission also found that the rules are exempt from
Texas Government Code, Chapter 2007 pursuant to §2007.003(b)(4) because
it is reasonably taken to fulfill an obligation mandated by federal law. The
commission has included elsewhere in this preamble its reasoned justification
for adopting this strategy and has explained why it is a necessary component
of the SIP which is federally mandated. This discussion, as well as the HGA
SIP which is being adopted concurrently, explains in detail that every rule
in the HGA SIP package is necessary and that none of the reductions in those
packages represent more than is necessary to bring the area into attainment
with the NAAQS. This rulemaking therefore meets the requirements of §2007.003(b)(4).
For these reasons the rules do not constitute a takings under Chapter 2007
and do not require additional analysis.
The purpose of the comment period is for the public to provide the commission
with information to say why they agree or disagree. To simply state that the
proposal did not meet the statute or that compliance with the proposed rules
is not technically or economically feasible does not provide the commission
with sufficient information to propose changes or alternative strategies.
There is no requirement that the commission determine the probable economic
cost of the unique aspects of every facility or source that must comply, nor
give the probable economic cost of every possible method of control. Rather,
the notice must include the cost of a reasonable method of compliance. Mere
disagreement with cost or technical feasibility estimates does not render
notice inadequate.
Small Business Analysis
The commission disagrees with the commenters and believes that it has complied
with Texas Government Code, §2006.002. Under that section the commission
is required to prepare a statement of the effect of the rules on small businesses,
including an objective assessment of the cost of compliance.
The purpose for performing the small business analysis and preparing the
resulting statement is twofold. First, it puts the affected community on notice
of the proposed rulemaking so that it can evaluate any potential fiscal impacts
and then provide that information to the commission for its consideration
prior to the commission's consideration of adoption of the rules. The second
purpose of the analysis is to prevent the agency from adopting rules that
would be unjustifiably burdensome to small businesses, while not similarly
impacting large businesses.
In keeping with the statutory requirement a cost analysis was performed
on these rules, and a statement of the analysis was published in the
Nevertheless, this lack of available economic data did not stop the agency
from doing its best to assess any potential economic impacts of the rules
on potentially affected businesses. While it is true that the commission was
unable to establish any definite cost figures, it did suggest, in the published
rule proposal, that small and micro-businesses "may have significant fiscal
implications" even though the amount could not be determined. The commission
did attempt to extrapolate, however, potential fiscal implications as a result
of comments received from North Central Texas Council of Governments (NCTCOG)
and TxDOT on the DFW construction shift proposal. Based on these comments,
the commission believes that costs associated with delays and extended construction
schedules could potentially be in the range of 15% - 20%.
Local Employment Impact
The commission agrees with the commenters that the proposed rule may affect
a local economy; however, it does not agree that it is the responsibility
of the commission to provide the local employment impact analysis. The APA
requires state agencies to determine whether a rule may affect a local economy
before proposing a rule for adoption. If the agency determines that a proposed
rule may affect a local economy, the agency must send a copy of the proposed
rule and other information to the Texas Workforce Commission before the agency
files notice of the proposed rule with the secretary of state. The APA requires
the Texas Workforce Commission to prepare a local employment impact statement
for proposed rules, if a state agency requests the statement. The Commission
determined that the proposed rule might affect a local economy, and sent the
proposed rule and other requested information to the Texas Workforce Commission.
The commission received a letter from the Texas Workforce Commission, indicating
that the Texas Workforce Commission did not have the ability to determine
the potential local employment impacts from the proposed rules.
ARTBA, AGC-Texas, AAR, ASLRRA, BFI, BCCA, EMA, ExxonMobil, Harris County,
HCIC, Union Pacific, and two individuals commented that the restrictions exceed
federal mandates and statutory authority without proper justification and
are therefore federally preempted and unlawful. The commission lacks statutory
authority to impose the workday shift on all the equipment covered by the
rule. The residual air quality benefit does not pass the practical and economically
feasible test that commission rules must meet. An agency such as the commission
must have legislative authority for its regulatory actions. The commission
cites as statutory authority for the construction workday shift, the Texas
Water Code, §5.103 (authority to adopt rules necessary to carry out its
purposes and duties under the Water Code and other laws of the state), the
TCAA, §§382.011 (authority to control the state's air), 382.012
(authority to develop a general, comprehensive plan for the control of the
state's air), 382.017 (authority to adopt rules consistent with the policy
and purposes of the TCAA), 382.019 (authority to adopt rules to control and
reduce emissions from engines used to propel land vehicles), and 382.039 (authority
to develop and implement transportation control programs and other measures
necessary to demonstrate attainment and protect the public from exposure to
hazardous air contaminants from motor vehicles). There is no specific statutory
authority for imposition of the workday shift. The only statutory provision
cited by the commission that deals with emissions from vehicles is §382.019
which is entitled "Methods Used to Control and Reduce Emissions From Land
Vehicles". Section 382.019(a) reads as follows: "The commission may by rule
provide requirements concerning the particular method to be used to control
and reduce emissions from engines used to propel land vehicles." Subsection
(a) is not authority to impose the workday shift because it is limited by
its terms to controlling and reducing emissions from engines used to propel
land vehicles. A prohibition against the operation of diesel engines in the
morning hours affects the timing of emissions from engines, and it may in
a general sense control emissions, but such a prohibition does not specifically
control and reduce them. The prohibition neither imposes limits upon emissions
nor does it reduce them. "Reduce" is the word the Legislature used in §382.019(a).
Unless that word is written out of the sentence, actions taken pursuant to §382.019
must "reduce" emissions. Notwithstanding the rationale for the workday shift
(theoretical reduction of ozone by shifting NO
x
emissions), the statutory authority in §382.019 is to reduce "emissions."
The same emissions of NO
x
(including particulates
and other materials produced by operation of diesel engines) are emitted either
before or after noon; moving them to a different part of the day does not
limit or reduce them. The language used in §382.019(a) is "control and
reduce." This phrase is conjunctive; it does not say control or reduce. Both
components must be present to be an exercise of the authority of §382.019(a).
The commission can only regulate emissions from engines that propel land vehicles.
The actions taken by the commission under §382.019(a) can lawfully only
apply to specific engines, "those used to propel land vehicles." This limitation
on the power of the commission is unambiguous. If an engine is not used to
propel land vehicles, the commission has no authority to regulate with respect
to that engine. However, the proposed workday shift covers a broader universe
of engines. Some units of covered equipment cannot move at all without being
towed or hauled on a trailer. These include crushing and processing equipment,
signal boards, cement and mortar mixers (those not truck mounted), and others.
Still other items of equipment can, in the broad sense, move as a result of
their engine being operated but such movement is incidental to the device's
function. Examples of these devices include: plate tampers, compactors and
rammers, pavers, trenchers, boring rigs, concrete saws (movement regulates
the speed of the blade through the material being sawed), surfacing equipment,
excavators, and certain cranes (which must be repositioned). The devices just
listed do not make use of an engine and transmission to move or propel themselves
in any normal sense and are not within the language of §382.019(a), and
the first list is certainly not. This point is reinforced by the definition
of the term "motor vehicle," found in the Texas Transportation Act:
In addition to Texas Health and Safety Code, §382.019, the commission
cites authority in §§382.011, 382.012, 382.017, and 382.039, all
of which provide specific authority for this rulemaking and are not "general
powers" of the agency. Section 382.019 specifically authorizes rules to reduce
emissions from engines used to propel land vehicles. As noted by the commenter,
engines subject to this rule are used, at least in part, to propel the equipment.
The statute doesn't limit the commission's authority to engines which are
used solely or primarily to propel engines. Therefore the commission asserts
that §382.019 does provide authority for the adoption of this rule. Additionally,
the presence of this authorization does not imply a lack of authority to control
emissions from other types of vehicles or equipment. For these reasons, the
commission disagrees that this rulemaking exceeds its statutory authority.
BFI commented that this rule violates the TCAA. Similar to its failure
to conduct an analysis compliant with the Texas Government Code, the commission
failed to conduct an analysis sufficient to determine the economic feasibility
of the six-hour ban and the public health and general welfare impacts of that
proposal as required by TCAA, §382.001 and §382.002.
The commission disagrees with the commenters and has made no change in
response to these comments. The proposed rules contained an analysis of information
available to the commission regarding the costs and benefits of the proposed
rules. This information met the statutory requirements of the TCAA and the
Texas APA because the information provided in the proposed rule was sufficient
for commenters to submit alternative assessments of the costs and benefits.
BFI also commented that the six-hour ban violates the Supremacy Clause
of the United States Constitution. Under the FCAA, the only two permissible
means by which states may establish emission control standards for non-road
engines and vehicles are the adoption of federal engine emission requirements,
or the adoption of California standards. Congress has occupied the field of
emission standards for non-road engines and vehicles and simultaneously prohibited
parallel and/or contradictory state regulations in that particular field.
By adopting this proposal, the commission has unlawfully adopted non-road
engine and vehicle emission requirements that expressly conflict with and
are thus preempted by §209 of the FCAA (42 USC, §7543(e)) and the
Supremacy Clause of the United States Constitution (art. 6, cl. 2). Recent
decisions by the federal courts have confirmed that the FCAA preemption provisions
apply to the full range of non-road engines and vehicles that will be affected
by the proposals at issue, and that the emission-related requirements established
under the proposal clearly constitute the type of requirements that states
are expressly preempted from adopting. See Engine Manufacturers Ass'n v. U.S.
EPA, 88 F.3d 1075 (D.C. Cir. 1996) and American Automobile Mfrs. Ass'n v.
Cahill, 152 F.3d 196, 200-01 (2d Cir. 1998).
The commission disagrees that these rules are preempted by federal law
because they do not propose to "adopt or attempt to enforce any standard relating
to the control of emissions," of any non- road engine or vehicle as described
in Section 209 of the FCAA. Instead, these rules will establish time-of-day
use restrictions on certain non-road diesel and industrial equipment rated
at 50 hp or more, between the hours of 6:00 a.m. and noon, from April 1 through
October 31. The rules do not in any way apply an emission control or emission
standard to any of the subject equipment, and therefore do not create any
emission-related requirements. Accordingly, the rules are not preempted under
the FCAA. Because there is no preemption under federal law, these rules also
do not violate the Supremacy Clause of the Constitution.
AAR, ASLRRA, and Union Pacific commented that the commission lacks authority
to restrict the ability of railroads to maintain their rights-of-way and operate
intermodal facilities, as per the Interstate Commerce Commission Termination
Act, which gives the Surface Transportation Board exclusive jurisdiction over
railroad transportation, including construction activities.
The commission disagrees with this comment and believes there is no conflict
between the scope of these rules and the scope of the jurisdiction actually
conferred to the Surface Transportation Board by the Interstate Commerce Commission
Termination Act.
ARTBA, AGC-Texas, BFI, BCCA, and HCIC commented that the FCAA expressly
prohibits Texas from claiming the intended SIP credit for the temporal emissions
shift (dispersion techniques) in this proposal. "Dispersion techniques" are
defined as "any intermittent or supplemental control of air pollutants varying
with atmospheric conditions." This proposal is a classic "dispersion technique"
because it shifts emissions in time to take advantage of varying atmospheric
conditions.
Ozone is formed through chemical reactions between natural and man-made
emissions of VOC and NO
x
in the presence of sunlight.
Higher ozone levels occur most frequently on hot summer afternoons. The critical
time for the mixing of NO
x
and VOCs is early
in the day. By delaying the hours of operation for construction equipment
and delaying the release of NO
x
emissions until
after noon during the ozone season, the NO
x
emissions
will not mix in the atmosphere with other ozone-forming compounds until after
the critical mixing time has passed. Therefore, production of ozone will be
stalled until later in the day when optimum ozone formation conditions no
longer exist, ultimately reducing the peak level of ozone produced.
This strategy is not dependent on atmospheric conditions to reduce ozone
formation, as such strategies are disfavored by FCAA, §7423. Instead,
the strategy creates reductions in the amount of NO
x
added to the atmosphere by construction equipment during the time
of day when those emissions have been shown to contribute to exceedances of
the ozone NAAQS. Use of "time of day" restrictions such as this for NAAQS
compliance strategies was supported by the EPA in their off-road mobile source
rules.
AGC-Texas, Baker Botts, Harris County, Union Pacific, and two individuals
commented that the EPA should accept responsibility for the late promulgation
of federal standards for non-road engines. The federal standards and their
implementation schedule are key in the effort to address emissions from construction
equipment. The commission has been forced to consider onerous strategies with
regard to these engines that are not economically feasible. The commission
should demand accountability from the EPA and be able to take credit for these
reductions.
Baker Botts commented that the commission should incorporate into the SIP
a greater level of reductions from federally preempted sources, such as low-sulfur
diesel, non-road Tier 2/Tier 3 heavy- duty engine standards. The EPA delays
in effectively regulating federally preempted sources have prompted the commission
to propose technically and economically infeasible emission reductions from
those sources in HGA that the state has authority to regulate to make up for
the missing reductions. Based on established legal precedent, the commission
and EPA have inherent authority to implement the intent of the FCAA by balancing
federal and state reductions in the SIP approval process. The HGA situation
warrants a flexible approach, due to both the uncertainties in acknowledging
the role of NO
x
reductions, and the EPA delays
in adequately controlling the federally preempted sources as required by the
FCAA.
Union Pacific commented that the EPA believes that a strong federal program
that addresses remanufacturing and in-use compliance best achieves the necessary
emission reductions. Also, a patchwork of state and local regulations would
be inefficient and hinder the EPA's ability to implement a uniform national
control program.
The commission agrees with the commenters that emission reductions from
federally preempted sources would provide benefits for the HGA SIP demonstration,
and the inability of the commission to regulate certain source categories
has necessitated the use of other ozone control strategies. However, the commission
understands that the EPA SIP approval process does not provide a mechanism
for credit for emission reductions that occur after the attainment date. The
commission understands that EPA is not currently considering accelerating
implementation schedules for existing federal rules. The commission is working
with EPA to determine the availability of SIP credit for many nontraditional
control strategy mechanisms, like economic incentive programs and flexibility
for preempted source categories. Additionally, the commission is working with
EPA to determine an appropriate federal contribution credit available for
the HGA SIP.
STATUTORY AUTHORITY
The new sections are adopted under Texas Water Code (TWC), §5.103,
which authorizes the commission to adopt rules necessary to carry out its
powers and duties under the TWC, and under Texas Health and Safety Code, TCAA, §382.017,
which provides the commission the authority to adopt rules consistent with
the policy and purposes of the TCAA. The new sections are also adopted under
TCAA, §382.011, which authorizes the commission to control the quality
of the state's air; §382.012, which authorizes the commission to prepare
and develop a general, comprehensive plan for the control of the state's air; §382.019,
which authorizes the commission to adopt rules to control and reduce emissions
from engines used to propel land vehicles; and §382.039, which authorizes
the commission to develop and implement transportation programs and other
measures necessary to demonstrate attainment and protect the public from exposure
to hazardous air contaminants from motor vehicles.
§114.482.Control Requirements.
No person shall start or operate any non-road diesel construction or
industrial equipment, of 50 horsepower and above, between the hours of 6:00
a.m. and noon, from April 1 through October 31, in the counties listed in §114.489
of this title (relating to Affected Counties and Compliance Dates.)
§114.486.Recordkeeping Requirements.
(a)
Any person that operates construction or industrial equipment
described in §114.482 of this title (relating to Control Requirements)
in those counties listed in §114.489 of this title (relating to Affected
Counties and Compliance Dates) is subject to requirements of this section.
(b)
Such person described in subsection (a) of this section
shall provide to the executive director, or other air pollution program with
jurisdiction, any records required to be maintained in accordance with this
section within five working days of a written request from the executive director,
or other air pollution program with jurisdiction.
(c)
Such person described in subsection (a) of this section
shall maintain daily operating records on the job site. These records must
be maintained for a minimum of two years. The records at a minimum must contain:
(1)
date(s) of operation;
(2)
start and end times of daily operation;
(3)
types of equipment being used; and
(4)
name(s) of the equipment operator(s).
§114.487.Exemptions.
(a)
The following uses of construction and industrial equipment
are exempt from §114.482 and §114.486 of this title (relating to
Control Requirements; and Record keeping Requirements) in the counties listed
in §114.489 of this title (relating to Affected Counties and Compliance
Dates):
(1)
equipment used exclusively for emergency operations to
protect public health and safety or the environment, including equipment being
used to repair facilities, devices, systems, or infrastructure that have failed,
or are in danger of failing, in order to prevent immediate harm to public
health, safety, or the environment; and
(2)
equipment used for mixing, transporting, pouring, or processing
of wet concrete provided such equipment is actually processing wet concrete.
(b)
Operators who submit an emissions reduction plan by May
31, 2002, which is approved by the executive director and the EPA no later
than May 31, 2003, will be exempt from operating hour restrictions upon implementation
of these rules in 2005, and will be permitted to operate during the restricted
hours. The executive director may allow plans to be submitted after May 31,
2002. In any event, a plan must be approved prior to the use of that plan
for compliance with the requirements of this division. In order to be approved,
the plan must demonstrate nitrogen oxide reductions equivalent to those required
by the rules being requested for exemption, and must contain adequate enforcement
provisions. The operators may submit a plan for exemption from the control
requirements of §114.472 of this title (relating to Control Requirements), §114.482
of this title, or both.
§114.489.Affected Counties and Compliance Dates.
Effective April 1, 2005, affected persons in the following counties
shall be in compliance with §§114.482, 114.486, and 114.487 of this
title (relating to Control Requirements; Recordkeeping Requirements; and Exemptions).
These include Brazoria, Fort Bend, Galveston, Harris, and Montgomery Counties.
This agency hereby certifies that the adoption has been reviewed
by legal counsel and found to be a valid exercise of the agency's legal authority.
Filed with the Office of the
Secretary of State on December 29, 2000.
TRD-200009078
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Effective date: January 18, 2001
Proposal publication date: August 25, 2000
For further information, please call: (512) 239-0348
Subchapter H. EMISSIONS BANKING AND TRADING
3.
MASS EMISSIONS CAP AND TRADE PROGRAM
4.
DISCRETE EMISSION CREDIT BANKING AND TRADING
Chapter 114.
CONTROL OF AIR POLLUTION FROM MOTOR VEHICLES
Subchapter H. LOW EMISSION FUELS
Chapter 114.
CONTROL OF AIR POLLUTION FROM MOTOR VEHICLES
Subchapter I. NON-ROAD ENGINES
6.
LAWN SERVICE EQUIPMENT OPERATING RESTRICTIONS
8.
HOUSTON/GALVESTON HEAVY EQUIPMENT FLEETS--COMPRESSION-IGNITION ENGINES
9.
HOUSTON/GALVESTON CONSTRUCTION EQUIPMENT OPERATING RESTRICTIONS
Subchapter J. OPERATIONAL CONTROLS FOR MOTOR VEHICLES