Part 1.
TEXAS NATURAL RESOURCE CONSERVATION COMMISSION
Chapter 101.
GENERAL AIR QUALITY RULES
The Texas Natural Resource Conservation Commission (commission) proposes
the repeal of §101.29, Emission Credit Banking and Trading. In addition,
the commission proposes 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.
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 PROPOSED 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. 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 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 has impacted the SIP
planning process is the revisions to the national ozone standard. 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 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 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 EPA in May 1998 became
complete by operation of law. However, 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 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 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 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 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,
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 included in
this proposal indicates that a gap of an additional 81 tons per day (tpd)
of NO
x
reductions is necessary for an approvable
attainment demonstration.
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 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.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses 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 Houston nonattainment area will need to ultimately reduce NO
x
more than 750 tons per day to reach attainment with the one-hour
standard. In addition, a VOC reduction of about 25% will have to be achieved.
The proposed 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 proposed rules to create incentives for the early
or permanent retirement of volatile organic compounds (VOC) and nitrogen oxides
(NO
x
) emissions. The intent of the proposed 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.
The proposed new §§101.300 - 101.304 are to be grouped into Subchapter
H, Division 1, Emission Credit Banking and Trading. The proposed rules consolidate
the requirements for generating, using, banking, and trading ERCs and MERCs.
The proposed rules are intended to achieve consistency between the rules governing
the use of ERCs/MERCs and DERCs and MDERCs. The proposed 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 proposed
sections would reduce the life of ERCs/MERCs generated after January 1, 2001
to five years to restrict the use of ERCs/MERCs to meet current environmental
conditions. The rules would 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.
The proposed new §§101.350 - 101.354, 101.356, 101.358 - 101.360
are to be grouped into Subchapter H, Division 3, Mass Emissions Cap and Trade
Program. These proposed sections will implement a mandatory annual NO
At this time, the commission proposes to 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.
The proposed new sections §§101.370 - 101.374 are to be grouped
into Subchapter H, Division 4, Discrete Emission Credit Banking and Trading.
The proposed rules consolidate the requirements for generating, using, banking,
and trading DERCs and MDERCs. The proposed rules are intended to achieve consistency
between the rules governing the use of ERCs/MERCs and DERCs/MDERCs. The proposed
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.
The commission solicits 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 solicits 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.
SECTION BY SECTION DISCUSSION
DIVISION 1
The proposed new §101.300 would contain 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 proposed to be transferred unchanged to §101.300.
The following definitions are proposed to be moved from §101.29 to §101.300
and amended. "Applicable emission point" would be 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 proposed rule language. The definition of "Baseline" would be 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" would be
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" would
be amended to refer to the source's rate of emissions per unit of activity
during the baseline activity period. The definition of "Curtailment" would
be 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)" would be 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, which can be applied to the emission reduction obligations of
another air quality source or to air quality attainment goals. "Most stringent
allowable emissions level" would be amended to include a reference to state
emission limits. The definition of "Ozone season" would be 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" would be amended to refer to replicable
and workable methods for mobile, stationary, or area sources. "Real reduction"
would mean a reduction in which actual emissions are reduced as opposed to
a reduction in allowable emissions. "Surplus" would be 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" would be 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 proposed for addition to §101.300.
"Baseline emissions" would be defined as the source's total actual emissions
based on the baseline activity and baseline emission rate. An "Emission credit"
would be newly defined as a credible emission reduction such as an "Emission
reduction credit" or "Mobile emission reduction credit." A new definition
of "Emission reduction" would be added as an actual reduction of emissions
from a stationary or mobile source. "Mobile emission baseline" would be newly
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 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" would be 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" would be newly defined as the mobile source's level of activity
during the applicable mobile source baseline year. "Mobile source baseline
emissions" would be newly defined as the mobile source's total emissions based
on the product of mobile source baseline activity and mobile source baseline
emission rate. "Source" would be 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.
The proposed 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 would be revised from the previous language in §101.29
to refer to both ERCs and MERCs as emission credits, unless the rule language
refers to specifically only one of these emission credits. This new section
would also state that participation in the program is voluntary.
The proposed new §101.302 would contain the general provisions for
the Emission Credit and Trading Program (Division 1). The wording of this
section would be 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. The certification requirements of an
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 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 would be 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 would be changed to be consistent with the previous
language of §101.29 for discrete emission credits. The changes would
allow for stationary sources (including area sources), mobile sources and
stationary sources (including area sources), and 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. Administratively
complete applications for ERCs which are 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 would allow 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 which is approved
by the executive director. To be consistent with the previous language of §101.29,
rule language would be 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. Recordkeeping requirements would be 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 would be 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 proposed which allows
the executive director to prohibit a company from participating in the program
if the company has violated or abused the program.
The proposed new §101.303 would outline the required protocols of
generating, calculating, certifying and registering, using, and transferring
emission credits. This section would require emission credits to be determined
based on established EPA protocols or when available, actual monitoring results
are calculated using good engineering practices. The existing procedures in §101.29
regarding the various means for generating emission credits would be 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 would be added which
does not allow the generation of credits if the emissions have been transferred
to another unit. This additional language would eliminate the potential of
a company shutting down a unit to generate emission credits, but altering
the operation of another piece of equipment to take the place of the shut
down unit and thereby increasing the emissions at the altered unit. The new
rules would 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. When applying for credits, new language would be 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 proposed
rules and to properly administer the program. As is currently stated in §101.29,
applicants will be notified in writing if the executive director denies the
application. Although it has been the commission's accepted practice, the
proposed new rule language specifically states that emissions credits will
be determined and certified to the nearest tenth of a ton per year. As is
currently stated in §101.29, the proposed section would state that emission
credits are determined and certified by using 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 is currently stated in §101.29, the
proposed section would list the mechanisms which can be used to make emission
credits enforceable. Rule language would be added which lists the OPCRE-1
form as an enforceable mechanism to establish new emission limits for grandfathered
sources when applying for emission credits. Proposed rule language would also
be 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 proposed 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 is currently stated in §101.29,
the proposed section will allow 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 proposed language
would add 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
would also allow for emission credits to be used for other provisions as allowable
within the guidelines of local, state, and federal laws. The proposed section
would allow 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, Trading, except
for the equations for determining 30-day rolling average emission limits,
would be changed to allow for emission reduction calculations in accordance
with the methodology of this new division. These revisions would replace the
former equations previously located in §117.570. The equations for calculating
30-day rolling average emission limits would be 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 would be revised to require the submittal of
the EC-3 Form. The timelines for the review of this submittal would be 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 would be retired as an environmental
contribution. The proposed section would state 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 would be 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 existing language in §101.29, which requires notification within
30 days of the transfer. As currently stated in §101.29, the proposed
section would state 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 proposed section would require applicants requiring 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 proposed section would require that
any other uses of credits be approved by the executive director prior to commencement
of the intended use. Rule language is proposed which would allow an applicant
to file a motion of reconsideration with the executive director within 60
days of denying a use of emission credits.
The proposed new §101.304 would require 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
The proposed new §101.350 would contain the definitions to be used
with Subchapter H, Emissions Credit Banking and Trading, Division 3, Mass
Emission Cap and Trade Program. The definition of "Allowance" would be the
authorization to emit one ton of NO
x
during a
control period. The definition of "Authorized account representative" would
be the responsible person who is authorized in writing, to transfer and otherwise
manage allowances. The definition of "Banked allowance" would be 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" would be 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" would be 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" would be the account where allowances held by a source or multiple
sources are recorded for the purposes of meeting the requirements of this
division. Sources not under common ownership or control may have separate
compliance accounts. The definition of "Control period" would be 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"
would be 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" would be, 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 predefined definitions: "Houston/Galveston
(HGA) ozone nonattainment area" as defined in §101.1; and "Source" as
defined in §101.1.
The proposed new §101.351 would state that the requirements of Division
3 apply to all stationary NO
x
sources in the
HGA nonattainment area subject to the emission specifications under §§117.106,
117.206, and 117.475 and that have a designed capacity to emit ten tons or
more per year of NO
x
.
The proposed new §101.352 would state that allowances may only be
used to meet the requirements of 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 would require that each source subject to this division shall
hold a quantity of allowances in its compliance account equal to or greater
than its total emission of NO
x
emitted during
the control period just ending. The cap and trade program would begin January
1, 2002. Beginning February 1, 2003, each source would be required to hold
the amount of allowance it used in the previous year's control period. The
new section would allow unused allowances to be banked as ERCs provided that
an enforceable and permanent reduction of annual allowances is approved by
the executive director, and all applicable requirements of Divisions 1 or
4 of Chapter 101, Subchapter H are met. The new section states that allowances
may be simultaneously used to satisfy offset requirements for new or modified
sources subject to federal nonattainment NSR requirements as provided in Chapter
116, Division 7 but not for netting requirements. The new section states that
all allowances would be allocated, transferred, or used as whole allowances
and that one compliance account shall be used for multiple sources located
at the same property and under common ownership or control. The new section
states that an allowance would not constitute a security or a property right.
The commission would maintain a registry of the allowances in each compliance
account. The registry would not contain proprietary information. Requests
for information identified as proprietary when submitted to the agency would
be subject to the procedures set out in the Texas Public Information Act.
The proposed new §101.353 describes how allowances will be allocated
to individual sources. Initially, for any source operating prior to January
1, 1997, allowances will be based on its actual level of activity averaged
over 1997, 1998, and 1999 multiplied by the higher of the source's actual
emission factor averaged over 1997, 1998, and 1999 (not to exceed any applicable
regulatory or permit limit) or the source's emission factor listed in Chapter
117. For a source not operating prior to January 1, 1997, but operating prior
to January 1, 2000, allowances will be equal to the source's actual level
of activity averaged over the most recent two consecutive calendar years (not
to exceed any applicable regulatory or permit limit) multiplied by the higher
of the source's actual emission factor averaged over the most recent two consecutive
calendar years (not to exceed any applicable regulatory or permit limit) or
the source's emission factor listed in Chapter 117. For a source authorized
under Chapter 106 or 116 but not operating prior to January 1, 2000, allowances
will be equal to the source's authorized level of activity multiplied by the
higher of source's authorized emission factor or the source'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. The purpose for using the higher of
the source's actual or allowable emission factor or its emission factor as
listed in Chapter 117 is to prevent penalizing those sources already emitting
or authorized to emit at levels equal to or lower than the requirements in
Chapter 117. For the 2003 and 2004 control periods, a source's allowances
will be reduced each year by one-third of the difference between its initial
allocation in 2002 and calculated final allocation for 2005. For the 2005
and subsequent control periods, allowances will be allocated based on historical
activity levels and emission factors as listed in Chapter 117 that are demonstrated
necessary to reach attainment. The section states that any new source which
has submitted an administratively complete application by January 2, 2001
will not be allocated any allowances. These new sources will be required to
obtain allowances from other sources already participating in the cap and
trade program or by obtaining DERC or MDERC. The section states that if a
source emits more NO
x
than what was held in the
compliance account on January 31 following the control period, that allocation
of allowances for the next control period will be reduced by the amount equal
to the emission exceeding the compliance account plus an additional 10%. The
section states that allowances would be allocated by January 1 of each control
period, beginning in 2002, and that the annual allocation of allowances may
be adjusted for any new SIP requirement and that allowances may be added or
subtracted from compliance accounts after reviewing the trading reports required
in §101.356 and the annual reporting requirements in §101.359. Proposed
language would allow the executive director to deviate from the allocation
methodology in extenuating circumstances.
The proposed new §101.354 describes how allowances will be subtracted
out of compliance accounts. The section states that allowances are deducted
in whole tons based on the source's level of activity during a control period
and multiplied by the source's emission factor during the control period.
The section states that a source 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 proposed 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
under proposed §101.353(a)(1)(C). The section states that allowances
that aren't expired or used could be traded at any time after they have been
allocated. Only authorized account representatives may trade allowances. Trade
requests would be made through the submittal of a completed form ECT-2. As
part of the application, the account representative shall report the price
paid per allowance. 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. Currently, the proposed §101.356(d)
only allows NO
x
credits to be used as an alternative
to allowances under the mass cap and trade program. The commission is soliciting
comments on how to address allowing certain VOC reductions which produce equal
or better ozone results in lieu of NO
x
reductions
for compliance with the cap.
The proposed new §101.358 states that if monitoring is required of
a source under a federal or state program, that monitoring or other data shall
be used to determine actual NO
x
emissions. Sources
not required to monitor shall calculate actual NO
x
emissions using good engineering practices, including calculation methodologies
in general use and accepted in NSR permitting.
The proposed new §101.359 states that sources shall submit by March
31 a completed ECT-1 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.
The proposed new §101.360 states that all sources required to participate
in the cap and trade program would be required to submit a completed ECT-3
certifying their historical level of activity by June 30, 2001. This information
will be used to calculate each source's allocations.
DIVISION 4
The proposed new §101.370 would contain 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 are proposed to be transferred unchanged to §101.370.
The following definitions are proposed to be moved from §101.29 to
this section and amended. "Applicable emission point" will be revised to refer
to the emission point generating an emission reduction or using an emission
credit. This revision would allow for consistency with the use of terms throughout
the proposed rule language. The definition of "Baseline" would be 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" would be
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" would
be amended to refer to the source's rate of emissions per unit of activity
during the baseline activity period. The definition of "Curtailment" would
be amended to mean a reduction in activity level at any stationary or mobile
source. The definition of "Discrete emission reduction credit" would be 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 proposed rules. The definition of "Ozone season" would be revised to
the portion of the year when ozone monitoring is federally required to occur
in a specific geographic area. "Protocol" would be amended to refer to replicable
and workable methods for mobile and stationary sources. The definition of
"Real reduction" would mean a reduction in which actual emissions are reduced
as opposed to a reduction in allowable emissions. "Surplus" would be 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" would be 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" would be revised to refer to the use of "emission
credits" which is more consistent with the terms in the proposed new rules.
The following new definitions are proposed for addition to §101.370.
"Baseline emissions" would be defined as the source's total actual emissions
based on the baseline activity and baseline emission rate. A "Discrete emission
credit" would be newly defined as a credible emission reduction such as a
"Discrete emission reduction credit" or "Mobile discrete emission reduction
credit." A new definition of "Emission reduction" would be added as an actual
reduction of emissions from a stationary or mobile area source. The "Generation
period" would be defined as the discrete period of time, not exceeding 12
months, over which a discrete emission reduction credit is created. A "Mobile
discrete emission reduction credit (MDERC or discrete mobile credit)" would
be 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. AMobile emissions "baseline" is proposed to be 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 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"
would be defined as the mobile source's level of activity during the applicable
mobile source baseline year. A definition for "Mobile source baseline emissions"
would be the source's total actual mobile source emissions based on the mobile
source activity and the mobile source emissions rate. "Most stringent allowable
emissions rate" would refer to the emission rate of a source, considering
all limitations required by applicable local, state, and federal regulations.
The term "Strategy activity" would be the source's level of activity during
the discrete emission reduction generation period and "Strategy emission rate"
would be the source's emission rate during the discrete emission reduction
generation period. "Source" would be 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.
The proposed 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 will be revised from the previous language in §101.29
to refer to both DERSs and MDERCs as discrete emission credits, unless the
rule language refers to specifically only one of these discrete emission credits.
This new section will also state that participation in the program is voluntary.
The proposed new §101.372 would contain the general provisions for
the Discrete Emission Credit and Trading Program. The wording of this section
will be 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 would specify to which
pollutants the program will apply and is unchanged from those currently in §101.29.
The section would state 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
would be added which prohibits emission credits certified as DERCs or MDERCs
from being recertified as emission credits under any other division within
Subchapter H. The proposed section would allow for stationary sources (including
area sources), mobile sources, and stationary sources (including area sources)
associated with agencies under §101.30 to be eligible to generate and
use emission credits, if there are no permits under the same account number
which contain a condition or conditions precluding the use of emission credits.
The proposed 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 and 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 proposed section states that DERCs and MDERCs may be used anytime after
certification and do not expire. The geographic scope will remain the same
as currently 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 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 currently stated in §101.29, the trading of discrete
emission credits may be discontinued by the executive director, in whole or
in part, with commission approval. As currently stated in §101.29 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 proposed section would require 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 currently 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 proposed 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 would be removed, since this program is currently ongoing.
The proposed new §101.373 outlines the required protocols of generating,
calculating, certifying and registering, using, and transferring discrete
emission credits. This section will require discrete emission credits, to
be determined based on established EPA protocols or when available, actual
monitoring results or calculated using good engineering practices. There are
no changes from the existing §101.29 regarding the various means for
generating discrete emission credits. The proposed section would revise 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 currently stated in §101.29, the proposed section would require DERCs
to be rounded down to the nearest ton. The proposed section limits the generation
period for DERCs to five years. The proposed section would not allow a source
to generate discrete emission credits for any emissions exceeding its allowable
emission limit. The proposed section deletes language from the existing §101.29
which restricted reductions used for netting from being generated as DERCs.
The proposed section states what requirements and data must be documented
to calculate MDERCs. The existing language located in §101.29 regarding
registration and certification of emission credits would remain the same and
would be relocated to this proposed section. The proposed section would add
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 proposed 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. Although it has always been
the accepted practice, the proposed new rule language specifically states
that discrete emissions credits will be determined and certified to the nearest
ton. The proposed section would include 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 proposed 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 proposed compliance and burden language is essentially
the same as currently 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.
There are no proposed changes to the existing §101.29 language regarding
what discrete emissions can or cannot be used for; however, the language would
be 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 proposed language would relocate 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. The commission proposes to
change 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 proposed for this division, and to add language which would
be consistent with the procedures and methodologies proposed within this division.
The equations for calculating 30-day rolling average emission limits would
be relocated to this section unmodified. There are no changes proposed 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 proposed section would include a list of the required
information to be submitted when a mobile source user intends to use discrete
emission credits. The proposed language listing the requirements for a user
to notify the executive director of actual discrete emission credit use would
remain 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 proposed language regarding compliance burden and enforcement for discrete
emission credit users would remain the same as previously stated in §101.29.
The proposed new §101.374 is a relocation, and there will be no wording
changes to previously existing language in §101.29, concerning auditing
of the DERC program.
FISCAL NOTE: COST TO STATE AND LOCAL GOVERNMENT
John Davis, Technical Specialist with Strategic Planning and Appropriations,
has determined for each year of the first five-year period the proposed amendments
are in effect, there will be fiscal implications which are not anticipated
to be significant for any single unit of state or local government as a result
of administration or enforcement of the proposed amendments.
The proposed amendments would consolidate existing requirements for generating,
using, banking, and trading ERCs, MERCs, DERCs, and MDERCs into two separate
programs. The section containing the original program would be repealed. The
two programs would be grouped under two divisions. Division 1, Credit Banking
and Trading, would handle ERC and MERC issues. Division 4, Discrete Emission
Credit Banking and Trading, would handle DERC and MDERC issues. The creation
of two separate programs would facilitate improved management and control
of the programs. The proposed amendments would update definitions, make administrative
changes to Divisions 1 and 4, and should provide flexibility and potential
cost savings in planning and determining the most economical mix of the application
of emission control technology with the use of emission credits to meet emission
reduction requirements.
In addition to creating Divisions 1 and 4, the proposed amendments would
create Division 3, The Mass Emission Cap and Trade Program. This program would
implement and manage a mandatory annual NO
x
emission
cap, phased-in between January 1, 2002 to January 1, 2005, on all existing
and new stationary sources located in the HGA ozone nonattainment area consisting
of: Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery,
and Waller Counties. The NO
x
emission cap only
affects sources in the HGA that have the capacity to emit ten tons of NO
The commission is required to submit a new SIP revision by the end of 2000
which will bring the HGA into attainment by 2007. The plan sets forth a control
strategy that provides emission reductions necessary for attainment and maintenance
of the national standards.
There will be fiscal impacts to state and local government facilities if
they elect to participate in the voluntary programs under Division 1 and 4
programs; however, the total number of state or local government sites affected
by these provisions is unknown. Division 1 covers facilities in nonattainment
counties and Division 4 covers facilities statewide. The costs associated
with participation in Division 1 and 4 programs would result from the purchase
of emission credits and would be dependent on the market value of the emission
credits. The current cost of credits in the HGA ranges from $750 per ton for
DERCs/MDERCs to $3,600 per ton per year for ERCs/MERCs. Actual costs will
be dependent on availability and demand. Total costs to state and local government
sites that elect to participate in Division 1 and 4 programs will depend on
the amount of emission credits purchased.
Although the total number is unknown, some of the approximately 6,000 pieces
of equipment at sources in the HGA that are affected by Division 3 provisions
will be owned and operated by state or local governments. 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 for
allowances will be dependent upon market demand and availability. The total
cost to state and local government sites will depend on the total number of
allowances purchased.
Most of the sources which will have to comply with the proposed rules are
currently subject to air permits and are already being inspected for compliance.
Consequently, only a limited number of additional facilities will need to
be inspected for compliance with the proposed amendments; therefore, there
are no significant fiscal implications for the agency as a result of implementation
of the proposed amendments.
PUBLIC BENEFIT AND COSTS
Mr. Davis has also determined for each of the first five years the proposed
amendments to Chapter 101 are in effect, the public benefit anticipated as
a result on implementing the amendments will be the reduction of emissions
of NO
x
in the HGA to a level that will allow
the area to meet the NAAQS for ozone.
The proposed amendments would consolidate existing requirements for generating,
using, banking, and trading ERCs, MERCs, DERCs, and MDERCs into two separate
programs. The section containing the original program would be repealed. The
two programs would be grouped under two divisions. Division 1, Credit Banking
and Trading, would handle ERC and MERC issues. Division 4, Discrete Emission
Credit Banking and Trading, would handle DERC and MDERC issues. The creation
of two separate programs would facilitate improved management and control
of the programs. The proposed amendments would update definitions, make administrative
changes to Divisions 1 and 4, and should provide flexibility and potential
cost savings in planning and determining the most economical mix of the application
of emission control technology with the use of emission credits to meet emission
reduction requirements.
In addition to creating Divisions 1 and 4, the proposed amendments would
create Division 3, The Mass Emission Cap and Trade Program. This program would
implement and manage a mandatory annual NO
x
emission
cap, phased in between January 1, 2002 to January 1, 2005, on all existing
and new stationary sources located in the HGA ozone nonattainment area consisting
of: Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery,
and Waller Counties. The NO
x
emission cap only
affects sources in the HGA that have the capacity to emit ten tons of NO
There will be fiscal impacts to persons and businesses if they elect to
participate in the voluntary programs under Division 1 and 4 programs; however,
the total number private entities affected by these provisions is unknown.
Division 1 covers facilities in nonattainment counties and Division 4 covers
facilities statewide. The costs associated with participation in Division
1 and 4 programs would result from the purchase of emission credits and would
be dependent on the market value of the emission credits. The current cost
of credits in the HGA area ranges from $750 per ton for DERCs/MDERCs to $3,600
per ton per year for ERCs/MERCs. Actual costs will be dependent on availability
and demand. Total costs to persons and businesses that elect to participate
in Division 1 and 4 programs will depend on the amount of emission credits
purchased.
There are approximately 6,000 pieces of equipment at sources in the HGA
that are affected by Division 3 provisions, some of which will be owned and
operated by persons and businesses. 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 for allowances will be
dependent upon market demand and availability. The total cost to persons and
businesses will depend on the total number of allowances purchased.
SMALL AND MICRO-BUSINESS ASSESSMENT
Adverse fiscal implications are not anticipated for small or micro-businesses
as a result of administration or enforcement of the proposed amendments. Under
the proposed amendments, small or micro-businesses electing to participate
in the program established by Divisions 1 and 4 would pay the same unit cost
for emission credits as other participants. There is no feasible way to reduce
the unit costs for small businesses. However, participation in this portion
of the program is voluntary. Under the Mass Emissions Cap and Trade Program
as established by Division 3, small or micro-businesses located in the HGA
would pay the same unit costs for the purchase of allowances as other businesses.
Of the 6,000 identified pieces of equipment at sources in the HGA, some will
be owned and operated by small or micro-businesses. Examples of likely equipment
at sources operated by small or micro-businesses include boilers, process
heaters, and internal combustion engines. The rules exempt sources which emit
less than ten tons per year. There is no feasible way to further reduce the
impact of the proposed amendments for small businesses.
DRAFT REGULATORY IMPACT ASSESSMENT
The commission has reviewed the proposed rulemaking in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225. Proposed
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. The proposed Division
3 would affect 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 proposed rulemaking in Division 3 of Chapter 101 meets
the definition of a "major environmental rule" as defined in Texas Government
Code, §2001.0225, but proposed rulemaking in Divisions 1 and 4 is 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. 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 January 31
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.
In addition, Texas Government Code, §2001.0225, only applies 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. This
rulemaking is not subject to the regulatory analysis provisions of §2001.0225(b),
because the proposed rule does not meet any of the four applicability requirements.
Specifically, the emission banking and trading requirements within this proposal
were developed in order to meet the ozone NAAQS set by the EPA under the Federal
Clean Air Act (FCAA), §7409, and therefore meet 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. 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 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. Thus, while specific measures are not generally required, the
emission reductions are required. 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.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code was amended by Senate Bill 633 (SB 633) during the
75th Legislative Session, 1999. The intent of SB 633 was to require agencies
to conduct a regulatory impact analysis (RIA) of extraordinary rules. These
are identified in the statutory language as 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. 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. For these reasons, rules proposed for
inclusion in the SIP fall under 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
reductions, such as those 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 obtain NO
x
emission reductions which 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 rulemaking does not exceed a standard
set by federal law, exceed an express requirement of state law (unless specifically
required by federal law), or exceed a requirement of a delegation agreement.
The rulemaking was not developed solely under the general powers of the agency,
but was specifically developed to meet the NAAQS established under federal
law and authorized under Texas Clean Air Act (TCAA), §§382.011,
382.012, and 382.017 as well as under 42 USC, §7410(a)(2)(A).
The commission invites public comment on the draft regulatory impact analysis.
TAKINGS IMPACT ASSESSMENT
The commission has completed a takings impact assessment for the proposed
rules. The following is a summary of that assessment. These sections are proposed
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 proposed 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 proposed sections do not meet the definition of a takings
under Texas Government Code, §2007.002(5). Although the proposed 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 partially fulfill a federal mandate under the FCAA, §7410.
Specifically, the emission limitations and control requirements within this
proposal 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 proposal 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. Consequently, the exemption
which applies to these proposed rules is that of an action reasonably taken
to fulfill an obligation mandated by federal law. Therefore, these proposed
revisions will not constitute a takings under Texas Government Code, Chapter
2007.
COASTAL MANAGEMENT PROGRAM CONSISTENCY REVIEW
The commission has determined the proposed 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'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 proposed 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
EFFECT ON SITES SUBJECT TO THE FEDERAL OPERATING PERMIT PROGRAM
The proposed new sections under Divisions 1, 3, and 4, if adopted, would
become part of the state's ozone attainment strategy; therefore, these amendments
would be submitted as part of the SIP. As a result, the proposed sections
and any allowances allocated under these sections would become applicable
requirements under the federal operating permit program.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El
Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments,
2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September
25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100
North I-35, Building E, Room 201S, Austin. The hearings are structured for
the receipt of oral or written comments by interested persons. Registration
will begin one hour prior to each hearing. Individuals may present oral statements
when called upon in order of registration. A four-minute time limit will be
established at each hearing to assure that enough time is allowed for every
interested person to speak. Open discussion will not occur during each hearing;
however, agency staff members will be available to discuss the proposal one
hour before each hearing, and will answer questions before and after each
hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend the hearings, should contact the Office
of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087,
faxed to (512) 239-4808, or emailed to
siprules@tnrcc.state.tx.us.
All comments should reference Rule Log Number 1998-089-101-AI. Comments
must be received by 5:00 p.m., September 25, 2000. For further information,
please contact Matthew R. Baker at (512) 239-1091 or Beecher Cameron at (512)
239-1495.
Subchapter A. GENERAL RULES
30 TAC §101.29
(Editor's note: The text of the following section proposed for
repeal will not be published. The section may be examined in the offices of
the Texas Natural Resource Conservation Commission or in the Texas Register
office, Room 245, James Earl Rudder Building, 1019 Brazos Street, Austin.)
STATUTORY AUTHORITY
The repeal is proposed under the 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 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.
The proposed repeal implements TCAA, §382.011, General Powers and
Duties; §382.012, State Air Control Plan; and §382.017, Rules.
§101.29.Emission Credit Banking and Trading.
This agency hereby certifies that the proposal has been
reviewed by legal counsel and found to be within the agency's legal authority
to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005653
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-4808
1.
EMISSION CREDIT BANKING AND TRADING
30 TAC §§101.300-101.304
STATUTORY AUTHORITY
The new sections are proposed under the 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.
The proposed new sections implement TCAA, §382.011, General Powers
and Duties; §382.012, State Air Control Plan; and §382.017, Rules.
§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 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, which can
be applied to the emission reduction obligations of another air quality source
or to air quality attainment goals.
(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.
§101.301.Purpose.
The purpose of this division is to allow the operator of a source to
generate emission credits by reducing emissions beyond the level required
by any local, state, and federal regulation and to allow the operator of another
source to use these credits. Participation under this division is strictly
voluntary.
§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.
(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 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 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.
(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 ton 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,
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;
(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 Office of Permitting, Remediation, and Registration.
(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 an 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 Office of Permitting, Remediation, and Registration
(OPRR). 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 OPRR 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 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 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 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 grants 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.
§101.304.Program Audits.
(a)
No later than three years after the effective date of this
division, 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 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 EPA and made available for public inspection within six months of the
date the audit begins.
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed
with the Office of the Secretary of State, on August 11, 2000.
TRD-200005654
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-1966
30 TAC §§101.350-101.354, 101.356, 101.358-101.360
STATUTORY AUTHORITY
The new sections are proposed under the 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.
The proposed new sections implement TCAA, §382.011, General Powers
and Duties; §382.012, State Air Control Plan; and §382.017, Rules.
§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
) 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 source or multiple sources are recorded for the purposes of meeting the
requirements of this division. Sources not under common ownership or control
may have separate compliance accounts.
(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,
and a corporation.
(11)
Source - As defined in §101.1 of this title.
§101.351.Applicability.
This division applies to all stationary nitrogen oxides (NO
x
) sources in the Houston/Galveston nonattainment area 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
§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 account, as defined in §101.1(1)
of this title (relating to Definitions), 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 the allowance system will begin with the initial control period beginning
January 1, 2002.
(c)
Unused allowances can be certified as emission reduction
credits, 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 to avoid
the applicability of federal and state new source review (NSR) requirements.
(e)
Allowances may simultaneously be used to satisfy offset
requirements for new or modified sources 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
as whole allowances. To determine the number of whole allowances, the number
of allowances will be rounded down when determining excess allowances and
rounded up when determining allowances used.
(h)
One compliance account shall be used for multiple sources
required to participate under this division and located at the same property
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 allocated according to the requirements
of this section.
(1)
For the 2002 control period in the Houston/Galveston (HGA)
nonattainment area:
(A)
for sources operating prior to January 1, 1997, allowances
will be equal to the source's actual level of activity averaged over 1997,
1998, and 1999 multiplied by the higher of the source's actual emission factor
averaged over 1997, 1998, and 1999 (not to exceed any applicable regulatory
or permit limit) or the source's emission factor listed in Chapter 117 of
this title (relating to Control of Air Pollution from Nitrogen Compounds);
(B)
for sources not operating prior to January 1, 1997, but
operating prior to January 1, 2000, allowances will be equal to the source's
actual level of activity averaged over the most recent two consecutive calendar
years multiplied by the higher of the source's actual emission factor averaged
over the most recent two consecutive calendar years (not to exceed any applicable
regulatory or permit limit) or the source's emission factor listed in Chapter
117 of this title.
(C)
for sources that have submitted an administratively complete
application under Chapter 116 of this title (relating to Control of Air Pollution
by Permits for New Construction or Modification) and for sources that qualify
for a permit by rule under Chapter 106 of this title (relating to Permits
by Rule), but not operating prior to January 1, 2000, allowances will be equal
to the source's authorized level of activity multiplied by the source's authorized
emission factor.
(2)
For the 2003 control period:
(A)
for sources with allowances allocated in accordance with
paragraph (1)(A) and (B) of this subsection the number of allocations shall
be two-thirds of the sum of the number of allocations derived in paragraphs
(1) and (4) of this subsection;
(B)
for sources with allowances allocated in accordance with
paragraph (1)(C) of this subsection, the number of allocations shall be determined
according to the following:
(i)
for sources operating prior to January 1, 2001, allowances
will be equal to the source's actual level of activity averaged over the most
recent two consecutive calendar years multiplied by two-thirds of the sum
of the higher of the source's actual emission factor averaged over the most
recent two consecutive calendar years (not to exceed any applicable regulatory
or permit limit) or the source's emission factor listed in Chapter 117 of
this title and the source's emission factor listed in Chapter 117 of this
title;
(ii)
for sources not operating prior to January 1, 2001, allowances
will be equal to the source's authorized level of activity multiplied by two-thirds
of the sum of the higher of the source's authorized emission factor or the
source's emission factor listed in Chapter 117 and the source's authorized
emission factor and the source's emission factor listed in Chapter 117.
(3)
For the 2004 control period:
(A)
for sources with allowances allocated in accordance with
paragraph (1)(A) and (B) of this subsection, the number of allocations shall
be one-third of the sum of the number of allocations derived in paragraphs
(1) and (4) of this subsection.
(B)
for sources with allowances allocated in accordance with
paragraph (1)(C) of this subsection, the number of allocations shall be determined
according to the following:
(i)
for sources operating prior to January 1, 2002, allowances
will be equal to the source's actual level of activity averaged over the most
recent two consecutive calendar years multiplied by one-third of the sum of
the higher of the source's actual emission factor averaged over the most recent
two consecutive calendar years (not to exceed any applicable regulatory or
permit limit) or the source's emission factor listed in Chapter 117 of this
title and the source's emission factor listed in Chapter 117 of this title;
(ii)
for sources not operating prior to January 1, 2002, allowances
will be equal to the source's authorized level of activity multiplied by one-third
of the sum of the higher of the source's authorized emission factor or the
source's emission factor listed in Chapter 117 of this title and the source's
authorized emission factor and the source's emission factor listed in Chapter
117 of this title.
(4)
For the 2005 and subsequent control periods allowances
will be calculated for each source using the following equation.
Figure: 30 TAC §101.353(a)(4)
(5)
For sources submitting applications for permits or qualifying
for a permit by rule after January 2, 2001, allowances for each control period
or the annual allocation rights shall be acquired from sources already participating
under this division, or in accordance with §101.356(d) of this title
(relating to Allowance Banking and Trading).
(6)
If actual emissions of NO
x
during a control period exceed the amount of allowances held in a compliance
account no later than January 31 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%.
(b)
Allowances will be allocated:
(1)
initially, by January 1, 2002;
(2)
subsequently, by January 1 of each following year by the
executive director, who will deposit allowances into each compliance account.
(c)
The annual deposit for any control period may be adjusted
to reflect new state implementation plan requirements.
(d)
Allowances may be added or deducted from compliance accounts
following the review of trading reports required under §101.356 of this
title.
(e)
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 source.
§101.354.Allowance Deductions.
(a)
Allowances will be deducted in whole tons from a source's
compliance account for a control period based upon the following equation.
Figure: 30 TAC §101.354(a)
(b)
On February 1 after every control period, a source 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 during a control period
may be banked for use in the following control period or traded except as
provided in subsection (b) of this section.
(b)
Allowances not used for compliance during a control period
which were allocated in accordance with §101.353(a)(1)(C) of this title
(relating to Allocation of Allowances) may not be banked for future use or
traded.
(c)
Allowances which have not expired may be traded at any
time after they have been allocated.
(1)
Only authorized account representatives may trade allowances.
(2)
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. 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.
(d)
Sources may use nitrogen oxides discrete emission credits
(DERCs or MDERCs) which have been generated, acquired, and used 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.
§101.358.Emission Monitoring and Compliance Demonstration.
(a)
Monitoring data or other emission quantifications for sources
required to monitor or quantify emissions under any other federal or state
program shall be used to show compliance with this division.
(b)
Sources 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, sources 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.
No later than June 30, 2001, the owner or operator of any source subject
to this division shall certify 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.
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed
with the Office of the Secretary of State, on August 11, 2000.
TRD-200005655
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-1966
30 TAC §§101.370-101.374
STATUTORY AUTHORITY
The new sections are proposed under the 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.
The proposed new sections implement TCAA, §382.011, General Powers
and Duties; §382.012, State Air Control Plan; and §382.017, Rules.
§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)
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.
(18)
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 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.
(19)
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).
(20)
Mobile source baseline activity--The mobile source's level
of activity during the applicable mobile source baseline year.
(21)
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.
(22)
Most stringent allowable emissions rate--The emissions
rate of a source, considering all limitations required by applicable local,
state, and federal regulations.
(23)
Ozone season--The portion of the year when ozone monitoring
is federally required to occur in a specific geographic area.
(24)
Permanent--An emission reduction that is long-lasting
and unchanging for the remaining life of the source.
(25)
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.
(26)
Quantifiable--An emission reduction that can be measured
or estimated with confidence using replicable techniques.
(27)
Real reduction--A reduction in which actual emissions
are reduced.
(28)
Source--As defined in §101.1 of this title (relating
to Definitions).
(29)
Shutdown--The permanent cessation of an activity producing
emissions at a facility.
(30)
Strategy activity--The source's level of activity during
the DERC generation period.
(31)
Strategy emission rate--The source's level of activity
during the DERC generation period.
(32)
Surplus--An emission reduction that is not otherwise required
of a source by a state or federal law, regulation, or agreed order.
(33)
Use period--The period of time over which the user source
applies discrete emission credits to an applicable emission reduction requirement.
(34)
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.
(35)
Use strategy--The compliance requirement for which discrete
emission credits are being used.
§101.371.Purpose.
The purpose of this division is to allow the operator of a source to
generate discrete emission credits by reducing emissions beyond the level
required by any local, state, and federal regulation, and to allow the operator
of another source to use these credits. Participation under this division
is strictly voluntary.
§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
10
) may qualify as discrete emission credits as appropriate. Reductions
of other criteria pollutants are not creditable. Reductions of one pollutant
may not be used to meet the reduction requirements for another pollutant,
except at such time as modeling demonstrates that one may be substituted for
another or as approved by the executive director.
(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) 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 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 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 Office of Permitting, Remediation, and Registration
(OPRR) 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 regulatiuons,
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 OPRR 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
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 EPA and made available for public inspection within six months after
the audit begins.
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed
with the Office of the Secretary of State, on August 11, 2000.
TRD-200005656
Margaret Hoffman
Director, Environmental Law Division
Earliest possible date of adoption:
For further information, please call:
30 TAC §§110.10, 110.12, 110.14, 110.15, 110.16, 110.17, 110.19
The Texas Natural Resource Conservation Commission (commission)
proposes new §110.10, Definitions; §110.12, Performance Standards; §110.14,
Technology Registration; §110.15, Testing Requirements; §110.16,
Labeling Requirements; §110.17, Exemptions; and §110.19, Affected
Counties and Compliance Schedules. The proposed new sections in new Chapter
110, Reduction of Air Pollution from Ozone, and corresponding revisions to
the state implementation plan (SIP) are proposed in order to reduce ground-level
ozone in the Houston/Galveston (HGA), Dallas/Fort Worth (DFW), and Beaumont/Port
Arthur (BPA) ozone nonattainment areas, as well as in the 95-county central
and eastern Texas region, and are one element of the strategy for the proposed
HGA Post-1999 Rate-of-Progress (ROP)/Attainment Demonstration SIP. The purpose
of these proposed rules is to incorporate a technology in the affected areas
that will reduce ozone from ambient air that is drawn across the external
heat exchanger units of air-cooled air conditioning units, including heat
pumps.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED 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. 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. 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 EPA on May 19, 1998, a revision to the HGA SIP which contained
the following elements in response to 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 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 control
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 covered 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 included in
this proposal indicates a gap of an additional 77.98 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 13.0 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 have formally submitted a resolution to
the commission, requesting the inclusion of many specific emission reduction
strategies.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses 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 solicits 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.
SECTION BY SECTION DISCUSSION
Chapter 110 is proposed as a new chapter which will contain rules to reduce
ambient levels of ozone directly rather than through the reduction of ozone
precursor chemicals.
Proposed new §110.10 includes new definitions for "covered air conditioning
unit," "inlet ozone concentration," "ozone reduction technology," "ozone reduction
efficiency," and "outlet ozone concentration."
Proposed new §110.12(a) sets performance standards for covered air
conditioning units that may be supplied or installed in the HGA, DFW, and
BPA ozone nonattainment areas after January 1, 2002. These requirements are
for the ozone reduction technology to have an initial ozone reduction efficiency
equal to or greater than 70%, and to retain an ozone reduction efficiency
equal to or greater than 50% averaged over any one-hour period, for a period
of 15 years. The requirements further mandate labeling of the covered air
conditioning units. Proposed new §110.12(b) prohibits persons from tampering
with, or knowingly disabling, ozone reduction technology on covered air conditioning
units.
Proposed new §110.14(a) requires persons supplying or manufacturing
ozone reduction technology to certify in a registration letter that each make
and model of covered air conditioning unit will be compliant with the performance
standards. Proposed new §110.14(b) clarifies that the ozone reduction
technology is not registered until the executive director provides the persons
supplying or manufacturing the ozone reduction technology with a written registration
confirmation letter and a registration number for each covered air conditioner.
Proposed new §110.14(c) provides the executive director the authority
to revoke or deny any registration if he determines that the technology does
not work.
Proposed new §110.15(a) establishes the testing requirements for determining
the ozone reduction efficiency for covered air conditioning units. The requirements
include the use of EPA reference methods for ozone concentration determination,
sets the range of ambient air inlet conditions under which the technology
must be able to show ozone reduction efficiency, and allows for testing in
artificially-created atmospheres, as well as ambient air, under properly controlled
conditions. Proposed new §110.15(b) allows the executive director to
approve alternate air sampling test methods so long as those methods are equivalent
to the methods listed in the section. Proposed new §110.15(c) clarifies
that the executive director is authorized to require the ozone reduction technology
manufacturer or supplier to conduct testing of any covered air conditioning
unit then in use.
Proposed new §110.16(a) requires covered air conditioning units to
be permanently labeled to identify that they are compliant with the rules.
The label must identify the unit's ozone reduction technology registration
number, the year and month of the unit's manufacture, and shall state whether
the unit meets the performance standards of §110.12.
Proposed new §110.17(a) allows the executive director to exempt a
manufacturer's covered air conditioning unit from specific rules in the chapter
if the manufacturer can prove that the technology is not available for, or
adaptable to, that unit.
Proposed new §110.19 lists the counties in which the rules apply,
and specifies a compliance date for those rules.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENTS
Mr. John Davis, Technical Specialist with Strategic Planning and Appropriations
determined for the first five-year period the proposed rules are in effect,
the commission does not anticipate significant fiscal implications for any
unit of state and local government as a result of administration or enforcement
of the proposed new sections.
The proposed rulemaking action would require that all air conditioning
units sold in the eight- county HGA, four-county DFW, and three-county BPA
ozone nonattainment areas and 95 additional central and eastern Texas counties
after January 1, 2002 have ozone reduction technology installed. The ozone
reduction technology must achieve an initial ozone reduction efficiency equal
to or greater than 70%, and an overall ozone reduction efficiency equal to
or greater than 50% averaged over any one-hour period, for a period of 15
years. Each new unit will have to be permanently labeled to identify that
it is compliant with the new requirements, and the manufacturers and suppliers
of ozone reduction technology will have to provide a registration letter to
the commission certifying that each make and model of covered air conditioning
unit will be compliant with the performance standards.
Any unit of state or local government in the affected counties that purchases
air conditioning units after January 1, 2002, will be affected by the proposed
rulemaking action. The commission anticipates that it will cost manufacturers
more to design and manufacture air conditioning units incorporating the ozone
reduction technology. Based on estimates provided by air conditioning manufacturers
and a potential ozone reduction technology manufacturer and supplier, affected
air conditioning units are projected to cost between $42 and $116 more per
ton of air conditioning capacity. Covered air conditioning units range in
size from 1.0 ton and less window units; 1.5 to 5.0 ton residential and small
commercial units; to 10 to 50 ton large air-cooled commercial units, such
as rooftop units. The resulting price increase would be $42 to $116 for typical
1.0 ton window unit, $63 to $580 for a typical residential unit, and $420
to $5,800 for large commercial units. The overall fiscal impact to state and
local governments is not anticipated to be significant unless a very large
number of the new air conditioning units are purchased.
PUBLIC BENEFIT AND COSTS
Mr. Davis also determined for each of the first five years the proposed
rules are in effect, the public benefit anticipated as a result on implementing
the new sections will be the reduction of ambient ground-level ozone concentrations.
The rules are expected to help the agency achieve the ozone NAAQS in the HGA,
DFW, and BPA nonattainment areas, as well as maintain the ozone NAAQS in the
central and eastern Texas region.
Under the proposed rulemaking, the commission will require that all air
conditioning units supplied or installed in the affected counties after January
1, 2002 have some type of ozone reduction technology, unless otherwise exempted.
The ozone reduction technology must achieve an initial ozone reduction efficiency
equal to or greater than 70%, and an overall ozone reduction efficiency equal
to or greater than 50% averaged over any one-hour period, for a period of
15 years. Each new unit will have to be permanently labeled to identify that
it is compliant with the new requirements and the manufacturers and suppliers
of ozone reduction technology will have to provide the agency a registration
letter certifying that each make and model of covered air conditioning unit
will be compliant with the performance standards.
Any individual or business in the affected counties that purchases covered
air conditioning units after January 1, 2002, will be affected by the proposed
rulemaking. The commission anticipates that it will cost manufacturers more
to design and manufacture air conditioning units incorporating the ozone reduction
technology. These increased costs will be offset by price increases to consumers.
Based on estimates provided by air conditioning manufacturers and a potential
ozone reduction technology manufacturer and supplier, affected air conditioning
units are projected to cost between $42 and $116 more per ton of air conditioning
capacity. Covered air conditioning units range in size from 1.0 ton and less
window units; 1.5 to 5.0 ton residential and small commercial units; to 10
to 50 ton large air- cooled commercial units, such as rooftop units. The resulting
price increase would be $42 to $116 for typical 1.0 ton window unit, $63 to
$580 for a typical residential unit, and $420 to $5,800 for large commercial
units. The overall fiscal impact to individuals and businesses will depend
on the number and capacity of new air conditioning units purchased.
SMALL AND MICRO BUSINESS ASSESSMENT
The commission does not anticipate adverse fiscal implications for small
or micro-businesses as a result of administration or enforcement of the proposed
new sections. The total fiscal impact to small or micro-businesses in the
affected counties will depend on how many air conditioning units they buy
or produce after January 1, 2002.
Under the proposed rulemaking, the commission will require that all air
conditioning units sold in the affected counties after January 1, 2002 have
ozone reduction technology installed. Incorporation of the new technology
will result in a price increase for air conditioners sold in the affected
counties after January 1, 2002. Small and micro-businesses in the affected
counties that purchase air conditioning units after January 1, 2002 can expect
to pay approximately $42 to $116 more per ton of air conditioning capacity.
Covered air conditioning units range in size from 1.0 ton and less window
units; 1.5 to 5.0 ton residential and small commercial units; to 10 to 50
ton large air-cooled commercial units, such as rooftop units. The resulting
price increase would be $42 to $116 for typical 1.0 ton window unit, $63 to
$580 for a typical residential unit, and $420 to $5,800 for large commercial
units.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the proposed rulemaking in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225, and determined
that the rulemaking action 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. Proposed new Chapter 110 is intended to protect the environment
or reduce risks to human health from environmental exposure to ozone and may
affect in an adverse material way, a sector of the economy, or competition.
However, the proposed rules do not meet any of the four criteria which
would cause them to be subject to Texas Government Code, §2001.0225(b).
Specifically, the ozone reduction technology required by the rules is part
of a plan to help meet the ozone NAAQS in the HGA, DFW, and BPA ozone nonattainment
areas. The rules are therefore being proposed to meet a federal requirement.
States are primarily responsible for ensuring attainment and maintenance of
NAAQS once the EPA has established those standards. Under 42 USC, §7410
and related provisions, states must submit, for EPA approval, SIPs that provide
for the attainment and maintenance of NAAQS. The proposed rules do not exceed
a requirement of a delegation agreement, and were not developed solely under
the general powers of the agency, but were specifically developed to meet
the air quality standards established under federal law as NAAQS and under
TCAA, §§382.002, 382.011, 382.012, 382.017, and 382.019.
TAKINGS IMPACT ASSESSMENT
The staff prepared a takings impact assessment for these rules in accordance
with Texas Government Code, §2007.043. The following is a summary of
that assessment. The specific purpose of the rulemaking is to require ozone
reduction technology on covered air conditioning units supplied or installed
in the HGA, DFW, and BPA ozone nonattainment areas, and the 95-county eastern
and central Texas region on or after January 1, 2002. This proposed rulemaking
is part of an air pollution strategy to reduce the level of ozone in those
areas. Promulgation and enforcement of the proposed rules will not burden
private, real property. Although the proposed rules do not directly prevent
a nuisance, do not prevent an immediate threat to life or property, and do
not prevent a real and substantial threat to public health and safety, they
do partially fulfill a federal mandate under 42 USC, §7410 requiring
states to develop and submit to the EPA a SIP which details the state's plans
for the attainment and maintenance of the NAAQS. Because the purpose of the
rule proposal is to require certain ozone reduction technology in order to
meet federal air quality standards for ozone it is exempted from the requirements
of Texas Government Code, §2007.043 as an action reasonably taken to
fulfill an obligation mandated by federal law. Consequently, this rulemaking
action does not constitute a takings under the Texas Government Code, Chapter
2007.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that the proposed 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 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), 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
goals and policies of the Coastal Coordination Council, and has determined
that they are consistent. The CMP goal applicable to this rule making action
is 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 ambient ozone concentrations
will be reduced as a result of these rules. The CMP policy applicable to this
rulemaking action is 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. Accordingly, the commission finds this rule making action to be consistent
with CMP goals and policies.
Interested persons may submit comments on the consistency of the proposed
rules with the CMP during the public comment period.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic
Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central
Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite
200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource
Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin.
The hearings are being held to receive oral and written comments from interested
persons. Registration will begin one hour prior to each hearing, and interested
persons may provide oral comments when called upon, in order of registration.
A four-minute time limit will be set at each hearing to assure that enough
time is allowed for every interested person to speak. Open discussion will
not occur during the hearings; however, agency staff members will be available
to discuss the proposal one hour before each hearing, and will answer questions
before and after each hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend a hearing, should contact the Office of
Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087,
faxed to (512) 239- 4808, or e-mailed to
siprules@tnrcc.state.tx.us
. All comments should reference Rule Log Number 2000-011J-110-AI. Comments
must be received by 5:00 p.m., September 25, 2000. For further information,
please contact Jeff Greif at (512) 239-1534 or Alan Henderson at (512) 239-1510.
STATUTORY AUTHORITY
The new sections are proposed under Texas Water Code (TWC or Code), §5.103,
which authorizes the commission to adopt rules necessary to carry out its
powers and duties under the Code, 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 proposed under TCAA, §382.002, which states as the policy and
purpose of the chapter the control or abatement of air pollution in the state; §382.011,
which authorizes the commission to control the quality of the state's air;
and §382.012, which authorizes the commission to prepare and develop
a general, comprehensive plan for the control of the state's air.
The proposed new sections implement TCAA, §382.002, relating to Policy
and Purpose; §382.011, relating to General Powers and Duties; and §382.012,
relating to State Air Control Plan.
§110.10.Definitions.
Unless specifically defined in the TCAA or in the rules of the commission,
the terms used by the commission have the meanings commonly ascribed to them
in the field of air pollution regulation. In addition to the terms which are
defined by the TCAA, the following words and terms, when used in this chapter,
shall have the following meanings, unless the context clearly indicates otherwise.
(1)
Covered air conditioning unit - Any air-cooled air conditioning
unit (including split or packaged units) or heat pump unit.
(2)
Inlet ozone concentration - The ozone concentration, measured
in parts per billion, of the air entering a covered air conditioning unit
prior to exposure to any ozone reduction technology.
(3)
Outlet ozone concentration - The ozone concentration, measured
in parts per billion, of air exiting a covered air conditioning unit.
(4)
Ozone reduction efficiency - The difference between inlet
ozone concentration and outlet ozone concentration, divided by the inlet ozone
concentration, expressed in percent.
(5)
Ozone reduction technology - A technology that converts
ozone into oxygen or removes ozone from the outdoor forced air flow through
a covered air conditioning unit without adding harmful air pollutants to the
ambient air.
§110.12.Performance Standards.
(a)
No person may supply or install a covered air conditioning
unit for use unless it is equipped with a registered ozone reduction technology
that has an initial ozone reduction efficiency equal to or greater than 70%
averaged over any one-hour period, retains an efficiency equal to or greater
than 50% averaged over any one-hour period for 15 years, and is properly labeled
in accordance with §110.16 of this title (relating to Labeling Requirements).
(b)
No person may tamper with, or knowingly disable, an ozone
reduction technology incorporated in a covered air conditioning unit in the
counties specified in §110.19 of this title (relating to Affected Counties
and Compliance Schedules).
§110.14.Technology Registration.
(a)
All persons supplying or manufacturing ozone reduction
technology for use in the counties specified in §110.19 of this title
(relating to Affected Counties and Compliance Schedules) must certify in writing
to the executive director that their ozone reduction technology will meet
the ozone reduction requirements of §110.12 of this title (relating to
Performance Standards) for each make and model of covered air conditioning
unit for which their technology is registered.
(b)
Each make and model of covered air conditioning unit is
registered when the ozone reduction technology manufacturer or supplier receives
a written registration confirmation from the executive director providing
a registration number for each covered air conditioning unit make and model.
(c)
The executive director may revoke, in writing, any registration
or part of a registration, if the executive director determines that the technology
does not meet the performance standards of §110.12 of this title.
§110.15.Testing Requirements.
(a)
Ozone reduction efficiency for covered air conditioning
units shall be determined in accordance with the following test methods and
procedures.
(1)
Ozone concentrations shall be determined by selecting and
using an appropriate EPA Reference Method from 40 Code of Federal Regulations
Part 50, Appendix D.
(2)
Ozone reduction technology must be demonstrated to meet
the ozone reduction efficiency performance standards in §110.12 of this
title (relating to Performance Standards), under all of the following conditions;
(A)
inlet ozone concentration between 60 - 140 parts per billion;
(B)
inlet air temperature between 75 - 110 degrees Fahrenheit;
(C)
inlet dew points between 50 - 75 degrees Fahrenheit; and
(D)
maximum and minimum air flow rates if applicable (fan on).
(3)
Ozone reduction efficiency shall be measured using one
or both of the following air sampling test methods:
(A)
simultaneous air sampling of the inlet and outlet ozone
concentration of a covered air conditioning unit for an hour where conditions
in the bulk air stream entering the unit are created by artificial means,
provided that:
(i)
sampling locations are chosen so that sufficient mixing
of the air enables sound ozone reduction measurements to be taken; and
(ii)
ozone is introduced and dispersed sufficiently upstream
of the covered air conditioning unit sampling location to insure complete
mixing in the air prior to the sampling point;
(B)
simultaneous air sampling of the inlet and outlet ozone
concentration of a covered air conditioning unit where ambient conditions
are within the ranges specified in paragraph (2) of this subsection for any
one-hour test run, provided that:
(i)
the probe locations are chosen in a manner which accurately
demonstrates the average ozone reduction efficiency of the ozone reduction
technology; and
(ii)
the probe locations are sufficiently shrouded to insure
the upstream and downstream measurements are taken from the same air mass
and that no cross mixing has occurred.
(b)
Alternate air sampling test methods may be used if the
executive director determines that the proposed methods are equivalent to
the methods listed in this section, and he approves the proposed method in
writing.
(c)
The ozone reduction technology manufacturer or supplier
must test, at their expense, any covered air conditioner in use in the nonattainment
area, within 90 days of being directed to conduct such testing by the executive
director.
§110.16.Labeling Requirements.
Covered air conditioning units intended for use in the counties specified
in §110.19 of this title (relating to Affected Counties and Compliance
Schedules) shall be labeled with a permanent material that must be welded,
riveted, or otherwise permanently attached to the unit. The label shall identify
the unit's ozone reduction technology registration number (if applicable),
the year and month of the unit's manufacture, and shall state whether the
unit meets the performance standards of §110.12 of this title (relating
to Performance Standards).
§110.17.Exemptions.
A covered air conditioning unit may be exempted from all or part of
this chapter, by the executive director in writing, if the air conditioning
unit manufacturer can demonstrate to the executive director's satisfaction
that no ozone reduction technology compliant with §110.12 of this title
(relating to Performance Standards) is available for, or adaptable to, any
of the covered air conditioning manufacturer's units
§110.19.Affected Counties and Compliance Schedules.
Effective January 1, 2002, persons subject to this rule in the following
counties shall be in compliance with §§110.12, 110.14 - 110.17 of
this title (relating Performance Standards; Technology Registration; Testing
Requirements; Labeling Requirements; and Exemptions):
(1)
Beaumont/Port Arthur counties including Hardin, Jefferson,
and Orange;
(2)
Dallas/Fort Worth counties including Collin, Dallas, Denton,
and Tarrant;
(3)
Houston/Galveston counties including Brazoria, Chambers,
Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller; and
(4)
East and Central 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.
This agency hereby certifies that the proposal has been
reviewed by legal counsel and found to be within the agency's legal authority
to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005631
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
The Texas Natural Resource Conservation Commission (commission) proposes
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 proposes 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.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED 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. 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
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. 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 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 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,
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 included in
this proposal indicates a gap of an additional 77.98 tons per day (tpd) of
NO
x
reductions is necessary for an approvable
attainment demonstration.
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.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses 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 proposed rules are one element of the control strategy for the HGA
Attainment Demonstration SIP. The purpose of these proposed 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 and DFW ozone nonattainment areas, and the 95-county central and
eastern Texas region.
The proposed revisions to the LED rules will require LED fuel statewide
for on-road use. In addition, the proposed 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 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 proposed rules. The proposed rules require that, beginning
May 1, 2002, diesel fuel produced for delivery and ultimate sale to the consumer
in the affected area does 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, the proposed 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 30 ppm sulfur beginning
May 1, 2004, and reduced again beginning May 1, 2006, to 15 ppm sulfur. Also,
the proposed rules require diesel fuel producers and importers who provide
fuel to the affected areas to register with the commission and provide quarterly
status reports.
The proposed rules will also revise definitions that will impact who is
affected by the proposed state LED fuel program as well as who is impacted
by the current requirements of the regional low Reid vapor pressure (RVP)
gasoline program, specified in §§114.301, 114.304 - 114.307, and
114.309. The proposed 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 proposing to expand the LED fuel ozone control strategy
which was developed for the DFW area and requires 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 proposed 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 2004 and then again in 2006. However,
although the EPA regulates diesel fuel content for on-road use, it does not
regulate the fuel content for non-road diesel fuel. Therefore, since there
is currently no federal limit on the content of non-road diesel, the state
has the authority to place controls on the fuel content of non-road diesel
fuel. As such, the commission is submitting, as part of the SIP, concurrent
with this proposed rulemaking, a request for a waiver in accordance with the
42 USC, §7545(C)(4)(c), for the on-road portion of these rules. The commission
does not believe that a waiver is needed for the non-road portion of these
rules. This proposed 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
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. The proposed 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. The proposed statewide coverage will
also provide a greater market for diesel fuel producers and importers to provide
the fuel required by these regulations and should help alleviate concerns
regarding out of area refueling practices.
The commission solicits 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 described in this proposal.
The commission solicits 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.
SECTION BY SECTION DISCUSSION
The proposed amendments to §114.6 contain revisions to the following
definitions: bulk plant, imported, import facility, and importer. The proposed
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 proposed
to be amended to "by truck or pipeline" to account for those bulk plants that
have pipeline delivery. The proposed amendments to the definitions of imported,
import facility, and importer are necessary to clarify that only those persons
who import fuel into the state are covered by these definitions. These proposed
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 proposed 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.
In addition, the proposed amendments to §114.6 contain new definitions
for motor vehicle and non-road equipment. Also, as a result of the new definitions,
the other existing definitions are to be renumbered accordingly.
The proposed 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 30 ppm and then
again to 15 ppm. In addition, the proposed amendments to §114.312 revise
subsection (g) to provide reference to the testing methods prescribed in the
proposed amendments to §114.315.
The proposed amendments to §114.313 clarify the language of subsection
(c) by adding commas in two locations.
The proposed amendments to §114.314 clarify language by adding the
word "fuel" after the phrase "low emission diesel (LED)." The proposed 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 proposed 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 proposed
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.
The proposed 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 proposed 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,
a new subsection (c) which establishes the compliance date and coverage area
for the sulfur content phase down to 30 ppm sulfur, and a new subsection (d)
which establishes the compliance date and coverage area for the sulfur content
phase down to 15 ppm sulfur.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT
John Davis, Technical Specialist with Strategic Planning and Appropriations,
determined that for the first five-year period the proposed amendments are
in effect there will be fiscal implications which are not anticipated to be
significant for any single unit of state and local government as a result
of administration or enforcement of the proposed amendments. The total annual
fiscal impact to statewide state and local government diesel vehicles is estimated
to be approximately $177 per year per diesel vehicle following implementation
of LED fuel standards on May 1, 2002 and an additional $177 per year per diesel
vehicle in the DFW, BPA, and HGA ozone nonattainment areas and 95 additional
central and eastern Texas counties, following the beginning of a desulfurization
phase in period which requires the sulfur level per gallon of gasoline to
be reduced from 30 ppm (May 1, 2004) to 15 ppm (May 1, 2006).
The proposed amendments to the current LED fuel rule will require LED fuel
statewide for on- road use. In addition, the proposed amendments will require
LED fuel for both on-road and non-road use in the eight-county HGA, four-county
DFW, and three-county BPA nonattainment areas along with 95 additional counties
in central and eastern Texas.
The HGA ozone nonattainment area consists of Brazoria, Chambers, Fort Bend,
Galveston, Harris, Liberty, Montgomery, and Waller Counties; the DFW ozone
nonattainment area consists of Collin, Dallas, Denton, and Tarrant Counties;
the BPA ozone nonattainment area consists of Hardin, Jefferson, and Orange
Counties; and the 95 additional central and eastern Texas counties are 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.
In order to comply with the proposed amendments, beginning May 1, 2002,
diesel fuel producers and importers must ensure diesel fuel distributed to
affected areas 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. Additionally, the proposed amendments will require the sulfur content
in the diesel fuel supplied to the DFW, BPA, and HGA nonattainment areas and
95 additional central and eastern Texas counties be reduced to 30 ppm sulfur
beginning May 1, 2004, and reduced again beginning May 1, 2006, to 15 ppm.
It is anticipated that the cost of producing diesel fuel to the May 1,
2002 standard will result in an estimated increase, in the cost for this fuel
at the pump, of $.04. Additionally, it is anticipated that owners and operators
of diesel fueled vehicles in counties affected by the May 1, 2006 standard
will have to pay an additional $.04 increase in diesel fuel prices, beginning
May 1, 2004, when the phase in period to desulfurize diesel from 30 ppm to
15 ppm sulfur content per gallon of diesel begins. The increase in fuel cost
for the May 1, 2002 standard was calculated in an analysis published by Northeast
States for Coordinated Air Use Management (NESCAUM) comparing the cost of
California diesel fuel to federal diesel. Federal diesel is the term used
for diesel fuel which meets federal standards and is used to fuel diesel-powered,
compression-ignition engines in on-road applications. The increase in fuel
cost for the May 1, 2006 standard is based on the EPA's "Notice of Proposed
Rulemaking on the Heavy-Duty Engine and Vehicle Standards and Highway Diesel
Fuel Sulfur Control Requirements." In addition, the proposed amendments will
require diesel fuel producers and importers who provide fuel to the affected
areas to register with the commission, test their fuel for compliance, and
provide quarterly status reports to the commission.
The following analysis in this fiscal note only considers on-road diesel
vehicles. Vehicle counts for non-road diesel vehicles are not available.
Statewide units of state and local government will likely be required to
pay an additional $.04 per gallon for diesel fuel that meets the proposed
LED requirements following the May 1, 2002 deadline. Approximately 12,261
state and local government diesel vehicles statewide consumed approximately
54 million gallons of diesel fuel in 1999. Based on a 1.5% growth rate, an
estimated 12,821 diesel vehicles would use approximately 57 million gallons
of on-road diesel fuel in 2002. The total annual fiscal impact to units of
state and local governments in 2002 would be approximately $1.5 million or
approximately $117 per diesel vehicle for 2002 (May - December 2002) and then
approximately $2.3 million or approximately $177 per year per diesel vehicle
afterward.
Beginning May 1, 2004, a desulfurization phase in period will begin, which
will eventually result in the reduction of sulfur content per gallon of diesel
from 30 ppm (May 1, 2004) to 15 ppm (May 1, 2006). All diesel gas sold in
the affected counties will have to meet the 15 ppm requirement by May 1, 2006.
Units of state and local government in the affected counties will likely be
required to pay an additional $.04 per gallon, for a total increase of $.08
beginning May 1, 2004, for diesel fuel that meets the stricter proposed LED
requirements. It is anticipated there will be approximately 9,600 state and
local government diesel vehicles operating in the affected areas by May 1,
2004. The additional fiscal impact for units of state and local government
vehicles operating in the affected counties in 2004 will be approximately
$1.1 million or approximately $117 per diesel vehicle for 2004 (May - December
2004) and then approximately $1.7 million or approximately $177 per diesel
vehicle per year afterward. The combined annual cost increase to units of
state and local governments which own or operate diesel vehicles in the affected
areas, for the first full years following implementation of fuel standards
associated with the May 1, 2002 and May 1, 2004 - 2006 phase-in period, is
approximately $3.3 million or approximately $354 per diesel vehicle per year.
PUBLIC BENEFIT AND COSTS
Mr. Davis also determined that for the first five years the proposed amendments
are in effect, the public benefit anticipated from enforcement of and compliance
with the proposed amendments will be the potential reduction of on-road and
non-road mobile source emissions, potentially improved air quality, and contribution
toward demonstration of attainment with the NAAQS for the HGA ozone nonattainment
areas. However, additional benefits will be achieved in the BPA and DFW ozone
nonattainment areas, and the 95-county central and eastern Texas region.
There are fiscal implications which are not anticipated to be significant
for any single owner or operator of diesel equipment as a result of administration
or enforcement of the proposed amendments. It is anticipated that LED diesel
fuel producers that supply fuel to the affected counties will incur additional
costs to produce diesel fuel that meets the proposed May 1, 2002 LED standards.
The cost of producing this LED fuel is estimated to be approximately $.04
per gallon more than for diesel fuel. Additionally, it is anticipated that
owners and operators of diesel fueled vehicles in counties affected by the
May 1, 2006 standard will be faced with an additional $.04 increase in diesel
fuel prices, beginning May 1, 2004, when the phase in period to desulfurize
diesel from 30 ppm to 15 ppm sulfur content per gallon of diesel begins.
The commission estimates that approximately 565,661 privately owned and
operated diesel vehicles statewide consumed approximately 2.5 billion gallons
of on-road diesel fuel in 1999. Based on a 1.5% growth rate, an estimated
591,499 privately owned and operated diesel vehicles would use approximately
2.6 billion gallons of on-road diesel fuel in 2002. The total fiscal impact
to persons and businesses which own and operate diesel vehicles statewide
in 2002 would be approximately $69 million or approximately $117 per diesel
vehicle for 2002 (May - December 2002) and then approximately $105 million
or approximately $177 per year per diesel vehicle afterward.
Beginning May 1, 2004, a desulfurization phase in period will begin, which
will eventually result in the reduction of sulfur content per gallon of diesel
from 30 ppm (May 1, 2004) to 15 ppm (May 1, 2006). All diesel gas sold in
the affected counties will have to meet the 15 ppm requirement by May 1, 2006.
Persons and businesses that own and operate diesel vehicles in the affected
counties will likely be required to pay an additional $.04 per gallon, for
a total increase of $.08 beginning May 1, 2004, for diesel fuel that meets
the stricter proposed LED requirements. The commission anticipates there will
be approximately 441,380 privately-owned diesel vehicles operating in the
affected counties by May 1, 2004. The additional fiscal impact for persons
and businesses that own and operate diesel vehicles operating in the affected
counties in 2004 will be approximately $51 million or approximately $117 per
diesel vehicle for 2004 (May - December 2004) and then approximately $78 million
or approximately $177 per diesel vehicle per year afterward. The combined
annual cost increase to persons and businesses which own or operate diesel
vehicles in the affected counties, for the first full years following implementation
of fuel standards associated with the May 1, 2002 and May 1, 2004 - 2006 phase
in period, is approximately $153 million or approximately $354 per diesel
vehicle per year.
There will be significant capital and operating costs to refineries to
meet the proposed May 1, 2006 standard. According to 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 and the average
annual operating cost would be approximately $8 million. These increased costs
will result in an anticipated $.04 per gallon increase in diesel fuel for
consumers beginning May 1, 2004. There are no anticipated significant additional
costs for diesel fuel producers and importers associated with registering
with the commission or supplying monthly status reports. Likewise, there are
no anticipated additional costs to producers for testing LED fuel because
producers are already testing their fuel for compliance with federal regulations
and industry standards.
SMALL AND MICRO-BUSINESS ASSESSMENT
There will be fiscal implications which are not anticipated to have an
adverse impact on any small or micro-businesses as a result of administration
or enforcement of the proposed amendments. There are no known diesel fuel
producers or importers that would be considered small or micro- businesses.
However, it is anticipated that many independent retailers of diesel fuel
statewide are small or micro-businesses. Therefore, production costs of approximately
$.04 per gallon for each standard (May 1, 2002 and May 1, 2004 - 2006) are
not anticipated to affect small or micro-businesses except for passing increased
costs of production through to consumers. The fiscal implications for small
and micro-businesses would include additional costs of approximately $.04
per gallon for LED starting May 1, 2002 and then an additional $.04 per gallon
for lower sulfur content diesel in counties affected by the May 1, 2004 -
2006 phase-in period standard. The additional costs would depend on the amount
of fuel used by the business. On an average basis, the annual cost to businesses
would be approximately $177 per diesel vehicle per year statewide and an additional
$177 per diesel vehicle per year in the counties affected by the May 1, 2004
- 2006 phase-in period standard.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the proposed rulemaking in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225, and determined
that the proposed rulemaking is subject to §2001.0225 because it could
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. 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. Although the proposed
amendments could meet the definition of a "major environmental rule" as defined
in the Texas Government Code, §2001.0225 only applies 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.
This proposed rulemaking action does not meet any of these four applicability
requirements. Specifically, the LED fuel requirements within these proposed
rules were developed in order to meet the ozone NAAQS set by the EPA under
42 USC, §7409, and therefore meet 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. 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 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. Thus, while specific measures are not generally required, the
emission reductions are required. 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.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code was amended by Senate Bill 633 (SB 633) during the
75th Legislative Session, 1999. The intent of SB 633 was to require agencies
to conduct a regulartory impact analysis (RIA) of extraordinary rules. These
are identified in the statutory language as 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. 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. For these reasons, rules proposed for
inclusion in the SIP fall under 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
reductions, such as those 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 obtain NO
x
emission reductions which 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 rulemaking does not exceed a standard
set by federal law, exceed an express requirement of state law (unless specifically
required by federal law), or exceed a requirement of a delegation agreement.
The rulemaking was not developed solely under the general powers of the agency,
but was specifically developed to meet the NAAQS established under federal
law and authorized under Texas Clean Air Act (TCAA), §§382.011,
382.012, 382.017, 382.019, 382.037(g), and 382.039.
The commission invites public comment on the draft regulatory impact analysis.
TAKINGS IMPACT ASSESSMENT
The commission prepared a takings impact assessment for these proposed
rules in accordance with Texas Government Code, §2007.043. The following
is a summary of that assessment. The specific purpose of the proposed rulemaking
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 to be able
to demonstrate attainment with the ozone NAAQS. Promulgation and enforcement
of the proposed rules may possibly burden private, real property because this
proposed rulemaking action may result in investment in the permanent installation
of new refinery processing equipment. Although the proposed 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 emission limitations and control requirements within this proposal have
been 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 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 proposed rules is to implement cleaner burning diesel fuel which is necessary
for the HGA ozone nonattainment area to meet the air quality standards established
under federal law as NAAQS. Consequently, the exemption which applies to these
proposed rules is that of an action reasonably taken to fulfill an obligation
mandated by federal law; therefore, these proposed rules do not constitute
a takings under the Texas Government Code, Chapter 2007.
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.
Therefore, in compliance with 31 TAC §505.22(e), the commission affirms
that this rulemaking action is consistent with CMP goals and policies.
Interested persons may submit comments on the consistency of the proposed
rules with the CMP during the public comment period.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic
Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central
Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite
200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource
Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin.
The hearings are structured for the receipt of oral or written comments by
interested persons. Registration will begin one hour prior to each hearing.
Individuals may present oral statements when called upon in order of registration.
A four-minute time limit will be established at each hearing to assure that
enough time is allowed for every interested person to speak. Open discussion
will not occur during each hearing; however, agency staff members will be
available to discuss the proposal one hour before each hearing, and will answer
questions before and after each hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend a hearing, should contact the Office of
Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087;
faxed to (512) 239- 4808; or emailed to
siprules@tnrcc.state.tx.us
. All comments should reference Rule Log Number 2000-011D-114-AI. Comments
must be received by 5:00 p.m., September 25, 2000. For further information,
please contact Morris Brown at (512) 239-1438 or Alan Henderson at (512) 239-
1510.
Subchapter A. DEFINITIONS
30 TAC §114.6
STATUTORY AUTHORITY
The amendment is proposed 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 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 amendment is also proposed 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.
The proposed amendment implements TCAA, §382.002, relating to Policy
and Purpose; §382.011, relating to General Powers and Duties; §382.012,
relating to State Air Control Plan; §382.019, relating to Methods Used
to Control and Reduce Emissions from Land Vehicles; §382.037(g), relating
to Vehicle Emissions Inspection and Maintenance Program; and §382.039,
relating to Attainment Program.
§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
[
(1)- (2)
(No change.)
(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)- (9)
(No change.)
(10)
Import
[
(11)
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
[
(12)
Importer - Any person who
imports motor vehicle fuel
[
(13)
(No change.)
(14)
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).
(15)
[
(16)
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.
(17)
[
(18)
[
(19)
[
(20)
[
(21)
[
(22)
[
(23)
[
This agency hereby certifies that the proposal has been
reviewed by legal counsel and found to be within the agency's legal authority
to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005615
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 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 proposed 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 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 proposed 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.
The proposed amendments implement TCAA, §382.002, relating to Policy
and Purpose; §382.011, relating to General Powers and Duties; §382.012,
relating to State Air Control Plan; §382.019, relating to Methods Used
to Control and Reduce Emissions from Land Vehicles; §382.037(g), relating
to Vehicle Emissions Inspection and Maintenance Program; and §382.039,
relating to Attainment Program.
§114.312.Low Emission Diesel Standards.
(a)
(No change.)
(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 30 ppm by weight per gallon in the counties specified
in §114.319(c) of this title.
(3)
The maximum sulfur content
of LED shall not exceed 15 ppm by weight per gallon in the counties specified
in §114.319(d) of this title.
(c)- (f)
(No change.)
(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) of this title (relating to Approved Test Methods)
[
§114.313.Designated Alternate Limits.
(a)- (b)
(No change.)
(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.
§114.314.Registration of Diesel Producers and Importers.
Each producer and importer that sells, offers for sale, supplies, or
offers for supply from its production facility or import facility low emission
diesel
fuel
(LED)
which may ultimately be used in
[
§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)- (5)
(No change.)
(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 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 subsection 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,
(A)
the average individual emissions of NO
(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.
§114.316.Monitoring, Recordkeeping, and Reporting Requirements.
(a)- (d)
(No change.)
(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
[
(1)- (5)
(No change.)
(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)
of this title.
(f)- (i)
(No change.)
§114.317.Exemptions to Low Emission Diesel Requirements.
(a)
(No change.)
(b)
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; 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.
§114.319.Affected Counties and Compliance Dates.
(a)
Beginning May 1, 2002, affected persons in
all
[
(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 May 1, 2004, 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.
(d)
Beginning May 1, 2006, affected
persons in the counties listed in subsection (b) of this section shall be
in compliance with §114.312(b)(3) 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 proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed
with the Office of the Secretary of State, on August 11, 2000.
TRD-200005614
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 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)
proposes 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 proposes 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 proposed HGA Post-1999 Rate-of-Progress (ROP)/Attainment
Demonstration SIP.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED 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. 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 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, 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,
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 EPA on May 19, 1998, a revision to the HGA SIP which contained
the following elements in response to 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 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 EPA in May 1998 became
complete by operation of law. However, 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 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 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 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 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,
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 included in
this proposal indicates a gap of an additional 77.98 tons per day (tpd) of
NO
x
reductions is necessary for an approvable
attainment demonstration.
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 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.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses 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 utilize ASM-2 and on-board diagnostic (OBD) technologies.
This proposed I/M program was modeled to cover the eight-county region comprising
the HGA nonattainment area. The proposed I/M program will reduce NO
x
emissions from on-road vehicles in the HGA ozone nonattainment area
by 42.03 tpd.
The proposed 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 proposed amendments addressed in this rule change are: changing the
testing technology in the HGA area to ASM-2 and OBD for Harris County beginning
May 1, 2002; Brazoria, Fort Bend, Galveston, and Montgomery Counties beginning
May 1, 2003; and Chambers, Liberty, and Waller Counties beginning May 1, 2004,
and an increase to the emissions inspection fee. The commission is proposing
a phase-in approach to make for a smoother implementation of the proposed
I/M program while still providing significant air quality improvements. In
addition, the proposed rules incorporate changes to the exhaust analyzer technical
specifications which will apply in every I/M program area.
The commission will take 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 proposed I/M program.
The estimated I/M NO
x
emission reductions for
Chambers County is .98 tpd, Liberty County .94 tpd, and Waller County is .77
tpd, for a combined estimated NO
x
emissions reduction
of 2.69 tpd. The commission will consider proposed alternatives during the
comment period and make a final determination. However, the remote sensing
component implemented in Harris County will likely continue to cover vehicles
registered in these counties even if an alternative control strategy is accepted
by the commission.
It is expected that EPA will soon publish a notice of proposed rulemaking
(NPRM) which will postpone the requirement to conduct OBD testing beginning
January 1, 2001, in I/M program areas for one year or more. In addition, it
is anticipated that EPA will propose dropping the tailpipe test for vehicles
receiving an OBD test (model year 1996 and newer) with no credit loss. The
commission may adjust OBD test requirements upon adoption of these rules,
based on information contained in the NPRM.
The commission solicits 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.
SECTION BY SECTION DISCUSSION
Proposed amendments to §114.50 establish revised program requirements
for the state I/M program for vehicle testing and inspection. The proposed
amendments to the program concern the applicability and control requirements.
The result of these amendments would be to incorporate the entire HGA nonattainment
area into the full I/M program in a phased manner.
Section 114.50(a)(4) is proposed to be amended by deleting "Harris County
of" the HGA program area. Subsection (a)(4)(A) and (B) is amended by adding
vehicles which are "registered and primarily operated in Harris County." Subsection
(a) is proposed to be amended by adding new paragraphs (4)(C) - (H) providing
clarification of program areas, model years to be tested, types of equipment
to be utilized, and implementation dates. New paragraph (4)(C) defines model
year vehicles to be tested using OBD in conjunction with ASM-2 in Harris County
beginning May 1, 2002. Paragraph (4)(D) defines model year vehicles to be
tested in Harris County using ASM-2, or a vehicle emissions test that meets
SIP emissions reduction requirements and is approved by EPA beginning May
1, 2002, and clarifies that testing stations must offer both an OBD and an
ASM-2 test. Paragraph (4) (E) defines model year vehicles to be tested using
OBD in conjunction with ASM-2 in Brazoria, Fort Bend, Galveston, and Montgomery
Counties beginning May 1, 2003. Paragraph (4)(F) defines model year vehicles
to be tested in Brazoria, Fort Bend, Galveston, and Montgomery Counties using
ASM-2, or a vehicle emissions test that meets SIP emissions reduction requirements
and is approved by EPA beginning May 1, 2003. Paragraph (4)(G) defines model
year vehicles to be tested using OBD in conjunction with ASM-2 in Chambers,
Liberty, and Waller Counties beginning May 1, 2004. Paragraph (4)(H) defines
model year vehicles to be tested in Chamber, Liberty, and Waller Counties
using ASM-2, or a vehicle emissions test that meets SIP emissions reductions
requirements and is approved by EPA beginning May 1, 2004. Paragraph (4)(H)
also clarifies that testing stations must offer both an OBD and an ASM-2 test.
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 proposed to be 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 proposed 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 establish the schedule for when motorists
in specific counties become eligible for waivers and extensions. The schedule
is consistent with the dates for the implementation of the emissions testing
program in each county.
Proposed amendments to §114.53 establish fee schedules for the different
counties which must be paid for the vehicle emissions inspection at an inspection
station. Subsection (a)(3) and (4) is proposed to be amended by revising test
methodology to ASM-2 and OBD and by adding counties to the I/M program beginning
May 1, 2002, and May 1, 2003, respectively. New subsection (a)(5) is being
proposed to provide for the collection of fees by those inspection stations
conducting ASM-2 and OBD testing beginning May 1, 2004.
In addition to the proposed amendments, the proposed 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.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT
John Davis, Technical Specialist with Strategic Planning and Appropriations,
determined that for the first five-year period the proposed rules are in effect,
the fiscal implication for affected units of state and local government, as
a result vehicle emission tests, is estimated to be an additional annual cost
of approximately $75,000 in the eight-county area consisting of Harris, Brazoria,
Fort Bend, Galveston, Montgomery, Chambers, Liberty, and Waller Counties.
The proposed amendments to Chapter 114 revise the vehicle emission 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 proposed
amendments are one element of the proposed HGA Post-1999 ROP/Attainment Demonstration
SIP. A SIP is a plan developed for any region where existing (measured and
modeled) ambient levels of pollutant exceeds the levels specified in a national
standard. The plan sets forth a control strategy that provides emission reductions
necessary for attainment and maintenance of the national standard.
The proposed amendments revise the I/M program using ASM-2 vehicle emission
testing equipment in the HGA ozone nonattainment area. Currently, only Harris
County requires an Enhanced I/M program. Galveston, Brazoria, Fort Bend, Montgomery,
Chambers, Liberty, and Waller Counties do not currently have an I/M program,
but will be required to have an Enhanced I/M program similar to Harris County
because they are in the HGA ozone nonattainment area. Harris County will use
ASM-2 emissions testing technology beginning May 1, 2002; Brazoria, Fort Bend,
Galveston, and Montgomery Counties will begin May 1, 2003; and Chambers, Liberty,
and Waller Counties will begin May 1, 2004.
In accordance with EPA requirements, the proposed amendments will require
an OBD check of all 1996 and newer model year vehicles subject to the I/M
requirements starting January 1, 2001. It is anticipated that owners of over
2.8 million vehicles in the HGA ozone nonattainment area could be affected
by vehicle emission inspections and other fee increases and the inspection
requirements in the proposed amendments. In addition, owners of vehicle safety
and emission inspection stations that choose to continue to perform emission
testing will be required to upgrade existing equipment or purchase new equipment
in order to comply with the proposed new emission test requirements incorporating
ASM-2 and OBD technology. There are currently 1,058 emission inspection stations
in Harris County. There are an additional 454 safety inspection stations in
Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller
Counties where the Enhanced I/M program will now be mandatory that will have
to purchase new analyzers. The cost to upgrade existing analyzers is $25,000
and the cost to purchase a new analyzer is $40,000.
A prior rulemaking increased the emission test fee in Harris County from
$13 to $14, effective January 1, 2001. The proposed amendments increase the
emission inspection fee in Harris County from $14 to $22.50 per inspection
effective May 1, 2002. Motorists, state and local government agencies, and
businesses owning registered vehicles in Harris County that are primarily
operated in the HGA ozone nonattainment area will be required to pay an additional
$8.50 for each emission inspection utilizing ASM-2 or OBD testing. Annual
emission testing is not currently required in Galveston, Brazoria, Fort Bend,
Montgomery, Chambers, Liberty, and Waller Counties. In the proposed amendments,
motorists, state and local government agencies, and businesses in Galveston,
Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties owning
registered vehicles that are primarily operated in the HGA ozone nonattainment
area will be required to pay $22.50 for an emission inspection utilizing ASM-2
or OBD technology.
Units of state and local government that own or operate vehicles subject
to I/M requirements in the HGA ozone nonattainment area will be required to
have emission testing and will be required to pay the fees established in
the proposed amendments. The fiscal impact on units of state and local government
associated with emission inspection costs are similar to the impacts on business
in general. Units of state and local government that own or operate vehicles
subject to I/M requirements in the HGA ozone nonattainment area will be able
to apply for a minimum expenditure waiver. The minimum expenditure to receive
a waiver in counties under the proposed I/M program will be $450. This is
no change in Harris County and a new $450 cost in Galveston, Brazoria, Fort
Bend, Montgomery, Chambers, Liberty, and Waller Counties. Based on the inspection
fee increase in Harris County and the inspection fee in the other counties,
the commission estimates that 6,300 state and local government vehicles in
HGA ozone nonattainment area will be affected with a total increased annual
cost of approximately $75,000.
PUBLIC BENEFIT AND COSTS
Mr. Davis also determined that for each year of the first five years the
proposed rules are in effect, the public benefit anticipated from enforcement
of and compliance with the proposed amendments will be the potential reduction
of on-road mobile source emissions, potential reduction in NO
x
emissions, potentially improved air quality, and contribution toward
demonstration of attainment with the ozone NAAQS.
There are economic implications anticipated to individuals and businesses
as a result of implementing the proposed amendments. Additional costs to affected
persons and businesses associated with the proposed amendments include increased
and additional costs associated with emission test fees, and additional costs
for inspection stations that opt to perform emission testing associated with
equipment upgrades or purchases. It is estimated that approximately 2.8 million
vehicles in the HGA ozone nonattainment area could potentially be affected
by the proposed amendments.
Individual motorists, state and local government agencies, and businesses
with vehicles subject to I/M requirements that are registered and primarily
operated in the HGA ozone nonattainment area will pay more to have their vehicle's
emissions tested incorporating OBD testing on their 1996 and newer vehicles.
Individual motorists, state and local government agencies, and businesses
with pre-1996 vehicles subject to I/M requirements that are registered and
primarily operated in the HGA ozone nonattainment area will pay more to have
their vehicle's emissions tested incorporating ASM-2 testing.
In the proposed amendments, the annual emission inspection fee is increased
from $14 to $22.50 in Harris County. Motorists, state and local government
agencies, and businesses owning registered vehicles in Harris County that
are primarily operated in the HGA ozone nonattainment area will pay $8.50
more for each emission inspection utilizing ASM-2 or OBD testing. Currently,
emission inspections are not required in Galveston, Brazoria, Fort Bend, Montgomery,
Chambers, Liberty, and Waller Counties. In the proposed amendments, motorists,
state and local government agencies, and business owning registered vehicles
in Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller
Counties that are primarily operated in the HGA ozone nonattainment area will
pay $22.50 for an annual emission inspection utilizing ASM-2 or OBD.
The cost to any person or business to comply with an enhanced I/M program
will vary depending upon the number of vehicles owned, the model year, and
the condition of the vehicle.
Businesses or individuals that own or operate vehicles subject to I/M requirements
in the HGA ozone nonattainment area will be able to apply for a minimum expenditure
waiver. The minimum expenditure to receive a waiver in counties under the
proposed I/M program will be $450. This is no change in Harris County and
a new $450 cost in Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty,
and Waller Counties.
Normally, the annual vehicle safety inspection and emission testing, where
required, is accomplished at the same facility. The decision by each inspection
facility to accomplish the proposed emission testing is voluntary and could
have economic implications. Safety inspection stations in the HGA ozone nonattainment
area that opt to perform emission testing for the I/M program would be required
to upgrade existing equipment or may have to purchase new equipment in order
to comply with the proposed new state emissions test requirements incorporating
OBD and ASM-2 testing. Current emission inspection stations in Harris County
that opt to continue to perform emission testing would be required to upgrade
existing equipment or may have to purchase new equipment to comply with the
proposed new state emissions test requirements incorporating ASM-2 and OBD
testing technology. It is anticipated that the economic decision to upgrade
or purchase the required equipment will include the economics of labor costs,
potential alternative use of labor's time, the equipment capital costs, and
volume of anticipated inspections, current equipment, and other anticipated
costs associated with emission testing. It is anticipated that some inspection
stations that must upgrade their equipment or purchase new equipment in order
to comply with the proposed emission testing requirements in the proposed
amendments will find it uneconomic to do so for various reasons and will be
unable to accomplish emission inspections. It is anticipated that this business
decision will be made by each inspection station.
According to Texas Department of Public Safety (DPS) records, there are
currently 1,058 inspection stations in Harris County. If these inspection
stations choose to perform emission testing, the commission staff estimated
that 10% (approximately 106) of the current inspection stations in Harris
County would have to purchase new ASM-2 equipment in order to conduct ASM-2
or OBD vehicle emission testing. Each new analyzer costs approximately $40,000.
If this equipment cost is capitalized, the monthly cost for the new equipment
is estimated to be approximately $900 per month for five years. The commission
staff also estimated that the remaining 90% (approximately 952) of the inspection
stations in Harris County could upgrade currently owned analyzers at a cost
of approximately $25,000. If this equipment cost is capitalized, the monthly
costs for the new equipment is estimated to be approximately $600 per month
for five years.
According to DPS records, there are 454 safety inspection stations in Galveston,
Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties where
the I/M program is proposed. All inspection stations in Galveston, Brazoria,
Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties will have to
purchase new analyzers to comply with the Enhanced I/M program. Each new analyzer
costs approximately $40,000. If this equipment cost is capitalized, the monthly
costs for the new equipment is estimated to be approximately $900 per month
for five years.
SMALL AND MICRO-BUSINESS ASSESSMENT
There are anticipated fiscal implications to small businesses and micro-businesses
as a result of implementing the proposed amendments. The fiscal implications
include increased minimum expenditure costs for waivers and increased costs
for emission testing of business-owned vehicles.
In general, the costs indicated in the public benefit portion of this fiscal
note for individuals, state and local government agencies, and businesses
will apply to small and micro-businesses. The minimum expenditure to receive
a waiver in counties under the proposed I/M program will be $450. This is
no change in Harris County and a new $450 cost in Galveston, Brazoria, Fort
Bend, Montgomery, Chambers, Liberty, and Waller Counties for the minimum expenditure
waiver.
The annual emission inspection fee will be $22.50 for counties under the
proposed I/M program in the HGA ozone nonattainment area. This is an increase
of $8.50 Harris County and a new $22.50 fee for the emission test Galveston,
Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties.
The cost to small and micro-businesses will vary with the number of vehicles
owned, model year, and condition of the vehicle(s).
In addition, it is anticipated that many of the inspection stations are
small or micro-businesses that will be required to upgrade their current testing
equipment or purchase new analyzers. New analyzer equipment required to conduct
ASM-2 (with integrated OBD) vehicle emission testing costs approximately $40,000.
The cost to upgrade currently owned analyzers to conduct ASM (with integrated
OBD) testing costs approximately $25,000. It is anticipated that the economic
decision to upgrade or purchase the required equipment will include the economics
of labor costs, potential alternative use of labor's time, the equipment capital
costs, and volume of anticipated inspections, current equipment, and other
anticipated costs associated with emission testing. It is anticipated that
some small or micro-business inspection stations that must upgrade their equipment
or purchase new equipment in order to comply with the proposed emission testing
requirements in the proposed amendments will find it uneconomic to do so for
various reasons and will be unable to continue emission inspections. It is
anticipated that this business decision will be made by each inspection station.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the proposed rulemaking in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225, and determined
that the rulemaking action is not subject to §2001.0225 because it 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. The proposed 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 proposed 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
proposed 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 proposed
amendments are one element of the proposed HGA Attainment Demonstration SIP.
As defined in the 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." 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. 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
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.
Thus, while specific measures are not generally required, the emission reductions
are required. 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.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code was amended by Senate Bill 633 (SB 633) during the
75th Legislative Session, 1999. The intent of SB 633 was to require agencies
to conduct a regulatory impact analysis (RIA) of extraordinary rules. These
are identified in the statutory language as 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. 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. For these reasons, rules proposed for
inclusion in the SIP fall under 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
reductions, such as those 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 obtain NO
x
emission reductions which 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 rulemaking does not exceed a standard
set by federal law, exceed an express requirement of state law (unless specifically
required by federal law), or exceed a requirement of a delegation agreement.
The rulemaking was not developed solely under the general powers of the agency,
but was specifically developed to meet the NAAQS established under federal
law and authorized under Texas Clean Air Act (TCAA), §§382.011,
382.012, 382.017, 382.019, 382.037 through 382.038, and 382.039.
The commission invites public comment on the draft regulatory impact assessment.
TAKINGS IMPACT ASSESSMENT
The commission prepared a takings impact assessment for these rules in
accordance with Texas Government Code, §2007.043. The following is a
summary of that assessment. The specific purpose of the rulemaking 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. 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 partially fulfill
a federal mandate under 42 USC, §7410. Specifically, the emissions limitations
and control requirements within this proposal 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 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 rulemaking action is to
implement a revised I/M program which is necessary for the ozone nonattainment
areas to meet the 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 takings under the Texas Government
Code, Chapter 2007.
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 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 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. Further, no new air contaminants will be authorized by the rule
revisions. Therefore, in compliance with 31 TAC §505.22(e), this rulemaking
is consistent with CMP goals and policies.
Interested persons may submit comments on the consistency of the proposed
rules with the CMP during the public comment period.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic
Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central
Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite
200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource
Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin.
The hearings are structured for the receipt of oral or written comments by
interested persons. Registration will begin one hour prior to each hearing.
Individuals may present oral statements when called upon in order of registration.
A four-minute time limit will be established at each hearing to assure that
enough time is allowed for every interested person to speak. Open discussion
will not occur during each hearing; however, agency staff members will be
available to discuss the proposal one hour before each hearing, and will answer
questions before and after each hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend the hearings, should contact the Office
of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087,
faxed to (512) 239- 4808, or emailed to
siprules@tnrcc.state.tx.us
. All comments should reference Rule Log Number 2000-011A-114-AI. Comments
must be received by 5:00 p.m., September 25, 2000. For further information,
please contact Bob Wierzowiecki, Technical Analysis Division, (512) 239-1769
or Alan Henderson, Policy and Regulations Division, (512) 239-1510.
STATUTORY AUTHORITY
The amendments are proposed under Texas Water Code, §5.103, which
provides the commission the authority to propose rules necessary to carry
out its powers and duties under the TWC. The amendments are also proposed
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 policy
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.
The amendments implement TCAA, §382.002, relating to Policy and Purpose; §382.011,
relating to General Powers and Duties; §382.012, relating to State Air
Control Plan; §382.019, relating to Methods Used to Control and Reduce
Emissions from Land Vehicles; §382.037 through §382.038, relating
to Vehicle Emissions Inspection and Maintenance Program; and §382.039,
relating to Attainment Program.
§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 Transportation 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)- (3)
(No change.)
(4)
This paragraph applies to all vehicles registered and primarily
operated in [
(A)
Beginning January 1, 2001, 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 in
conjunction with a TSI test.
(B)
Beginning January 1, 2001, all pre-1996 and older vehicles
registered and primarily operated in Harris County
shall be tested using
a TSI test. All vehicle emissions test stations must offer both TSI and OBD
tests to the public.
(C)
Beginning May 1, 2002, all
1996 and newer model year vehicles equipped with OBD systems and registered
and primarily operated in Harris County shall be tested using EPA-approved
OBD test procedures in conjunction with an ASM-2 test, or a vehicle emissions
test that meets SIP emissions reduction requirements and is approved by the
EPA.
(D)
Beginning May 1, 2002, all
pre-1996 model year vehicles registered and primarily operated in Harris County
shall be tested using the ASM-2 test, or a vehicle emissions test that meets
SIP emissions reduction requirements and is approved by the EPA. All vehicle
emissions test stations must offer both an OBD test and ASM-2 test, or a vehicle
emissions test that meets SIP emissions reduction requirements and is approved
by EPA, to the public.
(E)
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 in conjunction with
an ASM-2 test, or a vehicle emissions test that meets SIP emissions reduction
requirements and is approved by the EPA.
(F)
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. All vehicle emissions test
stations must offer both an OBD test and an ASM-2 test or a vehicle emissions
test that meets SIP emissions reduction requirements and is approved by the
EPA, to the public.
(G)
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 in conjunction with an ASM-2
test, or a vehicle emissions test that meets SIP emissions reduction requirements
and is approved by the EPA.
(H)
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. All vehicle emissions test stations must offer both an OBD test
and ASM-2 test, or a vehicle emissions test that meets SIP emissions reduction
requirements and is approved by EPA, to the public.
(5)
(No change.)
(b)
Control requirements.
(1)- (2)
(No change.)
(3)
Any motorist in the DFW, EDFW,
HGA,
or El Paso
program areas [
(4)- (7)
(No change.)
(c)- (d)
(No change.)
§114.51.Equipment Evaluation Procedures for Vehicle Exhaust Gas Analyzers.
(a)
Any manufacturer or distributor of vehicle testing equipment
may apply to the executive director of the Texas Natural Resource Conservation
Commission (commission) or his appointee, for approval of an exhaust gas analyzer
or analyzer system for use in the Texas Inspection and Maintenance (I/M) program
administered by the Texas Department of Public Safety. Each manufacturer shall
submit a formal certificate to the commission stating that any analyzer model
sold or leased by the manufacturer or its authorized representative and any
model currently in use in the I/M program will satisfy all design and performance
criteria set forth in "Specifications for Preconditioned Two Speed Idle Vehicle
Exhaust Gas Analyzer Systems for Use in the Texas Vehicle Emissions Testing
Program," dated
November 1
[
(b)- (e)
(No change.)
§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.
Application for waivers and extensions may be made in the following
inspection and maintenance program counties:
(1)
Motorists in Dallas, El Paso,
Harris, and Tarrant Counties are eligible for waivers and extensions.
(2)
Beginning May 1, 2002, motorists
in Collin and Denton Counties will be eligible for waivers and extensions.
(3)
Beginning May 1, 2003, motorists
in Brazoria, Ellis, Fort Bend, Galveston, Johnson, Kaufman, Montgomery, Parker,
and Rockwall Counties will be eligible for waivers and extensions.
(4)
Beginning May 1, 2004, motorists
in Chambers, Liberty, and Waller Counties will be eligible for waivers and
extensions.
(b)- (e)
(No change.)
§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)- (2)
(No change.)
(3)
Beginning May 1, 2002, any emissions inspection station
required to conduct an acceleration simulation mode
(ASM-2)
test
and test in accordance with §114.50(a)(2)(C) and (D)
and (4)(C)
and (D)
of this title shall collect a fee of $22.50 and shall remit
$2.00 to the DPS.
(4)
Beginning May 1, 2003, any emissions inspection station
required to conduct an
ASM- 2
[
(5)
Beginning May 1, 2004, any
emissions inspection station required to conduct an ASM-2 test and OBD test
in accordance with §114.50(a)(4)(G) and (H) of this title shall collect
a fee of $22.50 and shall remit $2.00 to the DPS.
(b)- (c)
(No change.)
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005612
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
3.
LOW SULFUR GASOLINE
30 TAC §114.322, 114.325 - 114.327, 114.329
The Texas Natural Resource Conservation Commission (commission)
proposes new §114.322, Control Requirements for Sulfur; §114.325,
Approved Sulfur Test Methods; §114.326, Testing and Recordkeeping Requirements; §114.327,
Exemptions; and §114.329, Affected Counties and Compliance Dates. The
commission proposes these new sections in Chapter 114, Control of Air Pollution
from Motor Vehicles; Subchapter H, Low Emission Fuels; new Division 3, Low
Sulfur Gasoline; and revisions to the state implementation plan (SIP) in order
to control ground-level ozone in the Houston/Galveston (HGA), Beaumont/Port
Arthur (BPA), and Dallas/Fort Worth (DFW) ozone nonattainment areas; and the
95-county central and eastern Texas region.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED 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. 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 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 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,
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 included in
this proposal indicates a gap of an additional 77.98 tons per day (tpd) of
NO
x
reductions is necessary for an approvable
attainment demonstration.
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.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses 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 proposed rules are one element of the control strategy for the HGA
Post-1999 ROP/Attainment Demonstration SIP. The purpose of these proposed
rules is to establish a regional LSG air pollution control strategy in the
counties located within the DFW, BPA, and HGA ozone nonattainment areas, and
in an additional 95 central and eastern Texas counties, to reduce NO
These proposed rules will implement a regional LSG program requiring gasoline
used for both on-road and off-road applications in the DFW, BPA, and HGA ozone
nonattainment areas and the 95-county central and eastern Texas region to
meet the LSG standards. The use of LSG will lower the emissions of NO
The proposed new LSG rules will require LSG for the eight HGA ozone nonattainment
area counties, which include Brazoria, Chambers, Fort Bend, Galveston, Harris,
Liberty, Montgomery, and Waller Counties; the four DFW ozone nonattainment
area counties, which include Collin, Dallas, Denton, and Tarrant Counties;
the three BPA ozone nonattainment area counties, which include Hardin, Jefferson,
and Hardin Counties; and the 95 central and eastern Texas region counties
which include 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 developed an LSG ozone control strategy which requires gasoline
content limits more restrictive than federal gasoline regulations. Currently,
the HGA and DFW ozone nonattainment areas are required to use federal reformulated
gasoline (RFG). In these areas, federal rules prohibit the sale of gasoline
which is not certified by the EPA as federal RFG. Consequently, gasoline in
these areas will have to continue to meet the federal RFG requirements in
addition to the proposed LSG rules. In addition to the federal RFG regulations,
the current federal regulations governing gasoline quality in Title 40 Code
of Federal Regulations (40 CFR) Part 80, Regulation of Fuels and Fuel Additives;
Subpart H, Gasoline Sulfur; §80.195, What Are the Gasoline Sulfur Standards
for Refiners and Importers?; establish limits for sulfur content in gasoline
used in motor vehicle applications. These federal regulations limit sulfur
in gasoline, beginning January 1, 2006, to a 30 ppm average and an 80 ppm
cap.
The commission is concurrently submitting, as part of the SIP and with
this proposed rulemaking, a waiver request in accordance with the 42 USC, §7545(c)(4)(C),
to implement this proposed LSG rule which is more stringent than the federal
sulfur control rules. This proposed waiver and SIP submittal is available
to the public by contacting Heather Evans at (512) 239-1970.
Modeling assessing the benefits of this NO
x
emission reduction strategy demonstrated that significant emission reductions
could be achieved from using an LSG as specified by the commission requirements.
By the year 2007, the LSG program will reduce NO
x
emissions in the HGA ozone nonattainment area by 1.15 tpd, and in all affected
areas by 4.98 tpd. The commission anticipates that production costs will increase
from $.03 to $.07 per gallon of gasoline to comply with the rules.
The commission solicits comment regarding the possible benefits of controlling
components of gasoline other than sulfur by which equivalent emission reductions
could be achieved as a possible alternative to the controls on sulfur as described
in this proposal.
The commission solicits 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.
SECTION BY SECTION DISCUSSION
The proposed new §114.322 establishes the control requirement that
the sulfur content in gasoline shall not exceed 15 ppm sulfur in the affected
areas. This 15 ppm state sulfur cap is more stringent than the federal 30
ppm average and 80 ppm cap.
The proposed new §114.325 establishes 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, or ASTM D5453-00 (Standard Test Method for Determination of Total
Sulfur in Light Hydrocarbons, Motor Fuels and Oils by Ultraviolet Fluorescence),
dated 2000, as the approved test methods to determine sulfur content in gasoline.
The proposed new §114.326 establishes the testing and recordkeeping
requirements for the LSG program. These proposed requirements stipulate that
producers and importers are required to test each batch of fuel for its sulfur
content, maintain records of this testing for two years, and include a certification
statement on the product transfer document that certifies that the fuel being
transferred into the affected areas meets the 15 ppm sulfur standard.
The proposed new §114.327 provides exemptions to the LSG program regulations.
These exemptions stipulate that gasoline solely intended for use as aviation
gasoline is exempt from the proposed sulfur standard, the owner or operator
of a retail fuel dispensing facility is exempt from the proposed testing requirements,
and gasoline that does not meet the proposed sulfur standard is not prohibited
from being transferred, placed, stored, and/or held within the affected counties
so long as it is not ultimately used to power a gasoline-fueled spark-ignition
engine in the affected counties.
The proposed new §114.329 establishes the compliance date and coverage
area that is required to comply with the requirements of the LSG program.
This section lists the affected counties for the DFW, BPA, and HGA ozone nonattainment
areas, and the counties included in the 95-county region.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT
John Davis, Technical Specialist with Strategic Planning and Appropriations,
determined that for the first five-year period the proposed new sections are
in effect, the commission anticipates no significant fiscal implications for
any single unit of state and local government as a result of administration
or enforcement of the proposed new sections. The commission estimates the
total annual fuel related fiscal impact to state and local governments in
the counties affected by the new sections to be approximately $20 to $47 per
vehicle per year following implementation of LSG fuel standards on May 1,
2004.
The proposed new sections will require LSG fuel for on-road and non-road
use within the eight-county HGA, the three-county BPA, and the four-county
DFW ozone nonattainment areas, along with 95 additional counties in the central
and eastern Texas region. The HGA ozone nonattainment area consists of Brazoria,
Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties;
the BPA nonattainment area consists of Hardin, Jefferson, and Orange Counties;
the DFW ozone nonattainment area consists of Collin, Dallas, Denton, and Tarrant
Counties; and the 95 additional central and eastern Texas counties include
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, Guadelupe,
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, Somerville,
Titus, Travis, Trinity, Tyler, Upshur, Van Zandt, Victoria, Walker, Washington,
Wharton, Williamson, Wilson, Wise, and Wood Counties.
The proposed new sections are one element of the proposed HGA Post-1999
ROP/Attainment Demonstration SIP. A SIP is a plan developed for any region
where existing (measured and/or estimated) ambient pollutant levels exceed
the level specified in a national standard. The plan establishes a control
strategy that provides emission reductions necessary for attainment and maintenance
of the national standards.
In order to comply with the proposed new sections, beginning May 1, 2004,
gasoline fuel producers and importers must ensure that all gasoline distributed
to affected areas shall not exceed 15 ppm sulfur.
The EPA analysis
Regulatory Impact Analysis: Control
of Air Pollution from Motor Vehicles: Tier 2 Vehicle Emissions Standards and
Gas Sulfur Control Requirements
and the responses to public comment
from the California Air Resource Board (CARB) regarding adoption of federal
Phase 3 gasoline standards, indicates that the anticipated cost of producing
gasoline to the May 1, 2004 standard will range from $.03 to $.07 per gallon.
The commission estimates that the increased production costs will raise the
cost for this fuel at the pump by $.03 to $.07 per gallon. In addition, the
proposed new sections will require gasoline producers and importers who provide
fuel to the affected areas to test their fuel for compliance with the standard,
maintain records for two years, and include certification statements regarding
sulfur content compliance on product transfer documents.
The proposed rules contain several exemptions to the LSG program regulations,
which are: gasoline solely intended for use as aviation gasoline is exempt
from the proposed LSG standards; the owner or operator of a retail fuel dispensing
facility is exempt from the proposed testing requirements; and gasoline that
does not meet the proposed LSG standard is not prohibited from being transferred,
placed, stored, or held within the affected counties as long as it is not
ultimately used to power a gasoline fueled spark-ignition engine in the affected
counties.
The following analysis in this fiscal note only considers on-road gasoline
powered vehicles. Vehicle counts for non-road gasoline powered vehicles is
not available.
Units of state and local government that own or operate gasoline powered
vehicles within the affected counties will likely be required to pay an additional
$.03 to $.07 per gallon for gasoline that meets the proposed LSG requirements
following the May 1, 2004 deadline. Approximately 48,992 state and local government
vehicles within the affected areas consumed approximately 33 million gallons
of gasoline in 1999. Based on a 1.5% growth rate, an estimated 52,778 gasoline
fueled vehicles would use approximately 36 million gallons of fuel in 2004.
The total annual fuel related fiscal impact to units of state and local governments
in 2004 would range from approximately $705,000 to $1.6 million or approximately
$13 to $31 per vehicle for 2004 (May -December 2004) and then approximately
$1 million to $2.5 million or approximately $20 to $47 per year per vehicle
afterward.
PUBLIC BENEFIT AND COSTS
Mr. Davis also determined that for the first five years the proposed new
sections are in effect, the public benefit anticipated from enforcement of
and compliance with the proposed new sections will be the potential reduction
of on-road and off-road mobile source emissions, contribution toward demonstration
of attainment and maintenance with the ozone NAAQS for the HGA, BPA, and DFW
ozone nonattainment areas, and potentially improved air quality for all counties
affected by the new sections.
The commission does not anticipate significant fiscal implications for
any single owner or operator of gasoline fueled vehicles as a result of administration
or enforcement of the proposed new sections. The commission anticipates that
gasoline producers that supply fuel to the affected counties will incur additional
costs to produce fuel that meets the proposed LSG standards. The cost of producing
this LSG fuel is estimated to be approximately $.03 to $.07 per gallon more
than for current gasoline. The commission estimates that gasoline prices will
increase by an additional $.03 to $.07 per gallon following implementation
of the proposed LSG standards.
The commission estimates that approximately 11,357,736 privately owned
and operated gasoline fueled vehicles in the affected counties consumed approximately
7.6 billion gallons of gasoline in 1999. Based on a 1.5% growth rate, an estimated
12,235,507 privately owned and operated gasoline fueled vehicles would use
approximately eight billion gallons of gasoline in 2004. The total annual
fuel related fiscal impact to units of individuals and businesses in the affected
areas in 2004 would range from approximately $163 million to $380 million
or approximately $13 to $31 per vehicle for 2004 (May -December 2004) and
then approximately $247 million to $578 million or approximately $20 to $47
per year per vehicle afterward.
The commission anticipates significant increases to capital and operating
costs in order for refineries to meet the proposed May 1, 2004 standard. An
estimated cost to refineries to decrease sulfur content in gasoline to 15
ppm is not available; however, an EPA cost study that shows the costs to refine
gasoline to 30 ppm provides an indication of the overall cost to refineries
to meet the May 1, 2004 15 ppm standard. According to EPA analysis found in
the
Regulatory Impact Analysis: Control of Air Pollution
from Motor Vehicles: Tier 2 Vehicle Emissions Standards and Gas Sulfur Control
Requirements
, the estimated capital costs for a typical refinery to
decrease the sulfur content in gasoline to 30 ppm would be approximately $44
million and the average annual operating cost would be approximately $16 million.
The commission anticipates no significant additional costs for gasoline producers
and importers associated with required records retention and certification
statements. Likewise, the commission anticipates no additional costs to producers
for testing LSG gasoline, because producers are already testing their fuel
for compliance with federal regulations and industry standards.
SMALL AND MICRO-BUSINESS ASSESSMENT
The commission does not anticipate fiscal implications which have an adverse
fiscal impact on any small business or micro-business as a result of administration
or enforcement of the proposed new sections. There are no known gasoline producers
or importers that would be considered small or micro-businesses. However,
the commission anticipates that many independent gasoline retailers within
the affected counties are small or micro-businesses. Therefore, production
costs of approximately $.03 to $.07 per gallon are not anticipated to affect
small or micro-business except to pass the increased costs of production through
to consumers. The fiscal implications for small or micro-businesses within
the affected areas would include additional costs of approximately $.03 to
$.07 per gallon for LSG beginning May 1, 2004. The total annual fuel-related
costs would depend on the amount of fuel used by the business. On an average
basis, the annual fuel-related cost to small or micro-businesses within the
affected areas would be approximately $20 to $47 per vehicle per year.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the proposed rulemaking in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225, and determined
that the proposed rulemaking is subject to §2001.0225 because it 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 new sections
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
new sections are intended to implement a LSG air pollution control program
as part of the strategy to reduce NO
x
emissions
necessary for the counties included in the eight-county HGA, three-county
BPA, and four-county DFW ozone nonattainment areas to be able to demonstrate
attainment and maintenance of the ozone NAAQS. The proposed new sections are
one element of the proposed HGA Post-1999 ROP/Attainment Demonstration SIP.
Although the proposed new sections meet the definition of a "major environmental
rule" as defined in the Texas Government Code, §2001.0225 only applies
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.
This proposed rulemaking action does not meet any of these four applicability
requirements. Specifically, the LSG requirements within these proposed rules
were developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409,
and therefore meet 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. 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
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.
Thus, while specific measures are not generally required, the emission reductions
are required. 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.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code was amended by Senate Bill 633 (SB 633) during the
75th Legislative Session, 1999. The intent of SB 633 was to require agencies
to conduct a regulatory impact analysis (RIA) of extraordinary rules. These
are identified in the statutory language as 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. 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. For these reasons, rules proposed for
inclusion in the SIP fall under 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
reductions, such as those 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 obtain NO
x
emission reductions which will
result in reductions in ozone formation in the HGA, BPA, and DFW ozone nonattainment
areas and the 95-county central and eastern Texas region, and help bring HGA
into compliance with the air quality standards established under federal law
as NAAQS for ozone. The rulemaking does not exceed a standard set by federal
law, exceed an express requirement of state law (unless specifically required
by federal law), or exceed a requirement of a delegation agreement. The rulemaking
was not developed solely under the general powers of the agency, but was specifically
developed to meet the NAAQS established under federal law and authorized under
Texas Clean Air Act (TCAA), §§382.011, 382.012, 382.017, 382.019,
382.037(g), and 382.039.
The commission invites public comment on the draft regulatory impact analysis.
TAKINGS IMPACT ASSESSMENT
The commission prepared a takings impact assessment for these proposed
rules in accordance with Texas Government Code, §2007.043. The following
is a summary of that assessment. The specific purpose of the proposed rulemaking
is to establish an LSG program which will act as an air pollution control
strategy to reduce NO
x
emissions necessary for
the eight-county HGA and the four-county DFW ozone nonattainment areas, to
be able to demonstrate attainment and maintenance of the ozone NAAQS. Promulgation
and enforcement of the proposed rules may possibly burden private, real property
because this proposed rulemaking action may result in investment in the permanent
installation of new refinery processing equipment. Although the proposed 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 emission limitations and control requirements within this
proposal have been 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 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 proposed rules is to implement cleaner burning gasoline which is necessary
for the HGA and DFW ozone nonattainment areas to meet the air quality standards
established under federal law as NAAQS. Consequently, the exemption which
applies to these proposed rules is that of an action reasonably taken to fulfill
an obligation mandated by federal law; therefore, these proposed rules do
not constitute a takings under Texas Government Code, Chapter 2007.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that the proposed 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 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.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic
Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central
Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite
200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource
Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin.
The hearings are structured for the receipt of oral or written comments by
interested persons. Registration will begin one hour prior to each hearing.
Individuals may present oral statements when called upon in order of registration.
A four-minute time limit will be established at each hearing to assure that
enough time is allowed for every interested person to speak. Open discussion
will not occur during each hearing; however, agency staff members will be
available to discuss the proposal one hour before each hearing, and will answer
questions before and after each hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend a hearing, should contact the Office of
Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, faxed to (512) 239-4808,
or emailed to
siprules@tnrcc.state.tx.us
.
All comments should reference Rule Log Number 2000-011F-114-AI. Comments must
be received by 5:00 p.m., September 25, 2000. For further information, please
contact Morris Brown at (512) 239-1438 or Alan Henderson at (512) 219-1510.
STATUTORY AUTHORITY
The new sections are proposed 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 proposed 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.
The proposed new sections implement TCAA, §382.002, relating to Policy
and Purpose; §382.011, relating to General Powers and Duties; §382.012,
relating to State Air Control Plan; §382.019, relating to Methods Used
to Control and Reduce Emissions from Land Vehicles; and §382.039, relating
to Attainment Program.
§114.322.Control Requirements for Sulfur.
No person shall sell, offer for sale, supply, or offer for supply,
dispense, transfer, allow the transfer, place, store, or hold in any stationary
tank, reservoir, or other container any gasoline containing more than 15 parts
per million sulfur, on a per gallon basis, which may ultimately be used to
power a gasoline-fueled spark-ignition engine in the counties listed in §114.329
of this title (relating to Affected Counties and Compliance Dates).
§114.325.Approved Sulfur Test Methods.
(a)
Compliance with the sulfur content requirements under §114.322
of this title (relating to Control Requirements for Sulfur) shall be determined
by applying 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, or ASTM D5453-00
(Standard Test Method for Determination of Total Sulfur in Light Hydrocarbons,
Motor Fuels and Oils by Ultraviolet Fluorescence), dated 2000.
(b)
Alternatives to the test methods prescribed in subsection
(a) of this section may be used if validated by 40 Code of Federal Regulations
63, Appendix A, Test Method 301 (effective December 29, 1992). For the purposes
of this paragraph, substitute "executive director" each place that Test Method
301 references "administrator."
§114.326.Testing and Recordkeeping Requirements.
(a)
Every producer or importer that has elected to sell, offer
for sale, supply, or offer for supply gasoline in counties listed in §114.329
of this title (relating to Affected Counties and Compliance Dates) is subject
to the requirements of this section.
(1)
Each producer or importer shall sample and test for the
sulfur content in each final blend of gasoline which the producer has produced
or imported, by collecting and analyzing a representative sample of gasoline
taken from the final blend, using the methodologies specified in §114.325
of this title (relating to Approved Sulfur Test Methods). If a producer or
importer blends gasoline 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 by the producer, 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 sulfur content. All gasoline
produced or imported by the producer or importer and not tested for sulfur
by the producer or importer as required by this section shall be deemed to
have a sulfur content exceeding the requirements in §114.322 of this
title (relating to Control Requirements for Sulfur), unless the producer or
importer demonstrates that the gasoline meets those requirements.
(2)
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 gasoline in accordance
with the requirements of this section, the final blend of gasoline shall be
presumed to have been sold or supplied by the producer or importer in violation
of the sulfur content requirements specified in §114.322 of this title.
(b)
For each final blend which is sold or supplied by a producer
or importer from their production or import facility, and which contains volumes
of gasoline that they have produced or imported and volumes that they neither
produced nor imported, the producer or importer shall establish, maintain,
and retain adequately organized records containing the following information:
(1)
the volume of gasoline in the final blend that was not
produced or imported by the producer or importer, the identity of the persons(s)
from whom such gasoline was acquired, the date(s) on which it was acquired,
and the invoice representing the acquisition(s);
(2)
the sulfur content of the volume of gasoline 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 gasoline represented in the final blend; or
(B)
written sampling results and gasoline testing supplied
by the person(s) from whom the gasoline was acquired; and
(3)
a producer or importer subject to subsection (b) 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.
(c)
All parties in the distribution chain (producers, importers,
terminals, pipelines, truckers, rail carriers, and retail fuel dispensing
outlets) subject to the provisions of §114.322 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, the 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)
the volume of gasoline being transferred;
(5)
the location of the gasoline at the time of transfer; and
(6)
the following certification statement: "This product complies
with the control requirements for sulfur specified in Title 30 Texas Administrative
Code §114.322, and may be used in any Texas county requiring gasoline
with a maximum sulfur content of 15 parts per million."
§114.327.Exemptions.
(a)
The following exemptions apply in the counties listed in §114.329
of this title (relating to Affected Counties and Compliance Dates).
(1)
All gasoline solely intended for use as aviation gasoline
is exempt from §114.322 and §114.326 of this title (relating to
Control Requirements for Sulfur; and Testing and Recordkeeping Requirements).
(2)
The owner or operator of a retail fuel dispensing facility
is exempt from all requirements of §114.326 of this title except §114.326(c)
of this title.
(b)
Gasoline that does not meet the requirements of §114.322
of this title is not prohibited from being transferred, placed, stored, and/or
held within the counties listed in §114.329 of this title so long as
it is not ultimately used to power a gasoline-fueled spark-ignition engine
in the affected counties.
§114.329.Affected Counties and Compliance Dates.
Beginning May 1, 2004, all affected persons in the counties listed
in paragraphs (1) - (4) of this section shall be in compliance with §§114.322,
114.325 - 114.327 of this title (relating to Control Requirements for Sulfur;
Approved Sulfur Test Methods; Testing and Recordkeeping Requirements; and
Exemptions):
(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.
This agency hereby certifies that the proposal has been
reviewed by legal counsel and found to be within the agency's legal authority
to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005646
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
30 TAC §§114.330 - 114.332, 114.336, 114.338, 114.339
The Texas Natural Resource Conservation Commission (commission)
proposes new §114.330, Definitions; §114.331, Applicability; §114.332,
Diesel Emulsion Standards; §114.336, Recordkeeping and Labeling; §114.338,
Registration; and §114.339, Affected Counties and Compliance Dates. The
commission proposes these revisions to Chapter 114, Control of Air Pollution
From Motor Vehicles; Subchapter H, Low Emission Fuels; new Division 4, Diesel
Emulsion Fuel; and corresponding revisions to the state implementation plan
(SIP) in order to control ground-level ozone in the Houston/Galveston (HGA)
ozone nonattainment area. These rules are designed to require use of a low-emission
diesel fuel formulation called diesel emulsion for both on- road and non-road
vehicles.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED 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. 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 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 area
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 EPA on May 19, 1998 a revision to the HGA SIP which contained
the following elements in response to 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 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,
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 included in
this proposal indicates a gap of an additional 77.98 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 10.70 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.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses 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
Diesel emulsion fuel is an emergent fuel technology that relies on a water-in-fuel
mixture to lower NO
x
emissions. The water content
lowers flame temperature by absorbing latent heat in the combustion chamber,
using the same principle of thermodynamics as injecting water into a turbine.
There are three components to diesel emulsion fuels: 1.) diesel fuel; 2.)
water, usually 10% to 20% by volume; and 3.) a diesel emulsion additive which
suspends the fuel and water together. The diesel emulsion fuel can be blended
by the diesel emulsion fuel distributor or blended on site using a fuel metering
system. According to preliminary laboratory results, the diesel emulsion additive
can lower exhaust NO
x
by 5.0% to 30%, irrespective
of the baseline fuel, depending on the engine configuration and operating
mode. At least one diesel emulsion additive has been approved for use by the
EPA.
Since the EPA does not require the addition of diesel emulsion additives
to diesel fuel, as is required by this proposal, the commission does not believe
that a waiver under 42 USC, §7445(c)(4)(C) is required.
The commission solicits 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.
SECTION BY SECTION DISCUSSION
New §114.330 contains the following definitions. "Diesel Emulsion
Additive" is defined as a type of diesel fuel additive which allows water
and diesel to be blended so that it does not separate. The additive may also
contain anti-freeze agents, cetane enhancers, and other ingredients as a water/fuel
mixture containing a diesel fuel additive to emulsify the water with the fuel,
usually in a mixture. "Diesel Emulsion Fuel" is defined as a water/fuel mixture
containing a diesel fuel additive to emulsify the water with the low emission
diesel fuel with the water. Typically, DEF contains 10% to 20% by volume water
and achieves an emission reduction of 5.0% to 30% NO
x
relative to the baseline diesel fuel depending concentration of water
in the fuel and engine design parameters. "Diesel Emulsion Fuel Distributor"
is defined as any person, retailer, jobber, bulk fuel reseller, low emission
diesel refiner who distributes diesel emulsion fuel to the ultimate user,
diesel emulsion additive manufacturer, or other entity who distributes diesel
fuel required to be mixed with a diesel emulsion additive. The proposed definition
of "Non-Road Heavy-Duty Engine" includes any non-road engines which are rated
over 175 nominal hp. This definition is intended to cover larger engines such
as bulldozers, graders, and cranes as well as locomotives, tugs, tow-boats,
and ferry boats. "On-road Heavy-duty Diesel Engine" is defined as a diesel
engine in a on-road vehicle which is greater than 10,000 pounds gross vehicle
weight rating (GVWR). The definition would exclude vehicles required to comply
with the federal Tier 2 engine standards. "Primarily Operated" is defined
as the use of a motor vehicle or engine more than 60 calendar days per year
in an affected county; it is presumed that an on-road vehicle is primarily
operated in the county in which it is registered.
Rule applicability is clarified in §114.331. The proposed new rule
would apply to distributors of on-road diesel with a throughput of at least
25,000 gallons per month at a fuel dispensing facility, such as a truck stop,
or vehicle fleet refueling station. It would apply to distributors of dyed
and undyed, non-road diesel with a throughput of at least 500 gallons of diesel
per month at one fuel dispensing facility, such as construction or agricultural
refueling. The diesel emulsion fuel distributors would make the diesel emulsion
fuel available to all on-road heavy-duty diesels, which are defined as being
greater than 10,000 pounds GVWR and all non-road engines rated over 175 nominal
hp. Any diesel fuel distributor who provides diesel fuel to owners or operators
of affected engines and equipment without inclusion of the diesel emulsion
fuel additive is considered in violation of this rule.
Diesel emulsion emission standards are specified in §114.332. The
diesel component of the diesel emulsion fuel must first meet low emission
diesel fuel requirements as required by §114.312, Low Emission Diesel
Standards. The requirement to use low emission diesel fuel is being proposed
elsewhere in this edition of the
Texas Register
for the HGA nonattainment area. Requiring use of low emission diesel fuel,
consistent with proposed §114.312, will provide a common baseline for
all users of the affected equipment and vehicles and will not require the
production of an alternative low emission diesel fuel. The diesel emulsion
additive must meet EPA requirements in 40 Code of Federal Regulations (CFR)
Part 80, Registration of Fuels and Fuel Additives. The amount, concentration,
or volume of water used in the diesel emulsion additive must be within the
manufacturer specifications. The diesel emulsion must result in emissions
that are 15% to 20% lower than the NO
x
emissions
in the base line fuel, depending on the types and operating mode of the engine,
and not result in a net increase in the other pollutant levels, as tested
by the manufacturer and approved or recognized by the EPA. Typically, diesel
emulsion fuel contains 10% to 20% by volume water and achieves an emission
reduction of 5.0% to 30% NO
x
relative to the
baseline diesel fuel, depending on the concentration of water in the fuel
and engine design parameters. The 15% and 20% reduction are a reasonable requirement
because significantly lower reductions would not be adequate to lower ozone
production in the photochemical modeling.
Recordkeeping and labeling are addressed in §114.336. All diesel emulsion
fuel distributors affected by this rule must retain some kind of proof of
purchase such as a fuel contract, leased blending facility, or receipts which
prove that the diesel emulsion fuel is actually being used. Also, any tanks
which are used to blend and/or dispense diesel emulsion fuel must be labeled
"DIESEL EMULSION FUEL ONLY," so as to differentiate between other fuel blends.
Registration is covered in §114.338. All diesel emulsion fuel distributors
affected by this rule are required to register with the executive director.
The registration must include a statement of acceptance of the requirements
of this rule and consent to allow the collection of samples of diesel emulsion
fuel and allow access to records. Registration will be on forms available
from the executive director.
Affected counties are addressed in §114.339. The counties covered
are in the HGA nonattainment area. The rules would be implemented on May 1,
2004.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT
John Davis, Technical Specialist with Strategic Planning and Appropriations,
has determined that for the first five-year period the proposed amendments
are in effect, there will be fiscal implications which may be significant
for units of state and local government located in the HGA area depending
on the number of affected on-road heavy-duty diesel vehicles and non-road
vehicles and equipment owned and operated as a result of administration or
enforcement of the proposed amendments. There should be no fiscal implications
to units of state and local government located outside of this nonattainment
area as a result of this proposed rules.
The proposed amendments require diesel emulsion fuel use for engines installed
in on-road heavy-duty diesel vehicles registered in HGA area with a GVWR greater
than 10,000 pounds or engines that are rated more than 175 hp installed in
non-road vehicles/equipment primarily operated in the HGA area. The proposed
amendments are limited to distributors of on-road diesel that dispense 25,000
or more gallons of diesel fuel per month at one fuel dispensing facility.
Additionally, the proposed amendments are limited to distributors of dyed
and undyed, non-road diesel that dispense 500 or more gallons of diesel fuel
per month at one fuel dispensing facility, such as construction or agricultural
refueling sites. The proposed rules would affect approximately 1,900 state
and local government and 53,000 privately owned and operated on-road heavy
duty diesel vehicles. Additionally, the proposed amendments would also affect
approximately 10,000 non-road vehicles/equipment.
Diesel emulsion fuel is an emergent technology for fuels which relies on
a water-in-fuel mixture to lower NO
x
emissions.
Diesel emulsion fuel is produced by blending diesel fuel, with water, and
a diesel emulsion additive which suspends the fuel and water together.
In order to achieve certain reductions, low emission diesel (LED) fuel
will be required to be blended with diesel emulsion fuel in the HGA area by
May 1, 2004. Standards for and results of using LED fuel are being presented
in a concurrent rulemaking. The commission requires that diesel emulsion fuel
used in on-road heavy-duty diesel engines has to result in a 15% decrease
in NO
x
compared to emission benefits from the
use of LED fuel alone. Additionally, the diesel emulsion fuel used in non-road
engines has to result in a 20% decrease in NO
x
compared to emission benefits from the use of LED fuel alone. Both uses should
not result in a net increase in any other pollutant. The diesel emulsion fuel
manufacturers have to provide the EPA with data that corroborates required
emission reductions.
Based on comments from a nationwide producer, diesel emulsion fuel will
cost the same per gallon as the diesel fuel component used to make the product,
because the increased cost of the additive is offset by the displacement of
fuel due to the inclusion of water in the overall mixture. By May 1, 2004,
the use of LED fuel in the HGA area will increase diesel fuel costs in the
HGA area by approximately $.08 more per gallon compared to today's current
regular diesel prices. The increased cost for LED fuel is based on analysis
published by Northeast States for Coordinated Air Use Management (NESCAUM)
and EPA's
Notice of Proposed Rulemaking on the Heavy-Duty
Engine and Vehicle Standards and Highway Diesel Fuel Sulfur Control Requirements
. In addition to the fuel-related cost, there may be an approximate
13% reduction in fuel economy as a result of using the fuel. Testing conducted
by one nationwide producer shows that fuel economy can decrease by as much
as 13%, but it can also stay the same depending on the vehicle and equipment
use.
If a unit of state or local government wants to dispense diesel emulsion
fuel, a special blending unit may be required. According to one nationwide
diesel emulsion fuel producer, a typical unit, which is capable of processing
over 5 million gallons a year, is used at major fuel distribution centers.
The cost for this type of unit is approximately $400,000 installed ($350,000
for the unit and $50,000 for installation). Final costs would depend on the
level of infrastructure at the proposed site (availability of water, electricity,
diesel fuel, platform, piping, etc.). The commission does not anticipate additional
costs to state and local government diesel emulsion fuel providers due to
required records retention, diesel emulsion fuel tank labeling, and registration
with the agency.
Units of state and local government will pay more to fuel affected vehicles
due to the increased cost of diesel emulsion fuel compared with current diesel
prices and the potential reduced gas mileage. Additionally, if a unit of state
or local government decides to dispense the fuel, a special blending unit
may have to be purchased or leased. The commission estimates that approximately
1,900 heavy-duty on-road diesel vehicles and a portion of the affected 10,000
non-road vehicles/equipment are owned and operated by state and local governments.
These vehicles would be required to use diesel emulsion fuel beginning May
1, 2004. Based on a 25,000 vehicle miles traveled (VMT) per year the total
annual cost for units of state and local government affected by the proposed
amendments would increase by $775 per diesel vehicle per year. There will
be a cost increase associated with using diesel emulsion fuel in non-road
vehicles/equipment; however, the total amount cannot be determined at this
time. Total costs to units of state and local government in affected counties,
not including blending unit and related infrastructure costs and non-road
vehicles/equipment, would be approximately $1.4 million.
PUBLIC BENEFIT AND COSTS
Mr. Davis also has determined that for the first five years the proposed
amendments are in effect, the public benefit anticipated from enforcement
of and compliance with the proposed amendments will be the potential reduction
of on-road and non-road mobile source emissions, potentially improved air
quality, and contribution toward demonstration of attainment with the NAAQS
for the HGA area.
The commission estimates there may be significant fiscal impacts for owners
and operators of on- road heavy-duty diesel vehicles and non-road diesel vehicles/equipment
affected by the proposed amendments. The proposed rules require diesel emulsion
fuel use in engines installed in on-road heavy-duty diesel vehicles registered
in the HGA area with a GVWR greater than 10,000 pounds and in engines rated
greater than 175 hp installed in non-road vehicles/equipment primarily operated
in the HGA area. The proposed rules would affect approximately 53,000 privately
owned and operated on- road heavy-duty diesel vehicles and a portion of the
10,000 affected non-road vehicles/equipment that are privately owned and operated.
Diesel emulsion fuel is an emergent technology for fuels which relies on
a water-in-fuel mixture to lower NO
x
emissions.
Diesel emulsion fuel is produced by blending diesel fuel, with water, and
a diesel emulsion additive which suspends the fuel and water together.
In order to achieve certain reductions, LED fuel will be required to be
blended with diesel emulsion fuel in the HGA area by May 1, 2004. Standards
for and results of using LED fuel are being presented in a concurrent rulemaking.
The commission requires that diesel emulsion fuel used in on- road heavy-duty
diesel engines has to result in a 15% decrease in NO
x
compared to emission benefits from the use of LED fuel alone. Additionally,
the diesel emulsion fuel used in non- road engines has to result in a 20%
decrease in NO
x
compared to emission benefits
from the use of LED fuel alone. Both uses should not result in a net increase
in any other pollutant. The diesel emulsion fuel manufacturers must provide
the EPA with data that corroborates required emission reductions.
Based on comments from potential producers, diesel emulsion fuel will cost
the same per gallon as the diesel fuel component, because the increased cost
of the additive is offset by the displacement of fuel due to the inclusion
of water in the overall mixture. By May 1, 2004, the use of LED fuel in the
HGA area will increase diesel fuel costs by approximately $.08 more per gallon
compared to today's current regular diesel prices. Therefore, diesel emulsion
fuel sold after May 1, 2004 should cost approximately $.08 more per gallon.
In addition to the fuel-related cost increases, there may be an approximate
13% reduction in fuel economy as a result of using diesel emulsion fuel. Testing
conducted by one producer shows that fuel economy can decrease by as much
as 13%, but it can also stay the same. The overall fuel economy effect is
dependent on vehicle/equipment use.
The proposed amendments will probably directly affect major fuel distribution
centers that serve the affected counties and individuals and businesses that
want to dispense diesel emulsion fuel to affected vehicles and equipment in
the affected counties, because a special blending unit will probably have
to be used in order to mix the diesel emulsion fuel. According to one nationwide
diesel emulsion fuel producer, a typical unit, which is capable of processing
over five million gallons a year, is used at major fuel distribution centers.
The cost for this type of unit is approximately $400,000 installed ($350,000
for the unit and $50,000 for installation). Final costs would depend on the
level of infrastructure at the proposed site (availability of water, electricity,
diesel fuel, platform, piping, etc.). The commission does not anticipate additional
costs to individuals and businesses that are diesel emulsion fuel providers
due to required records retention, diesel emulsion fuel tank labeling, and
registration with the agency.
Individuals and businesses will probably pay more to fuel affected vehicles
due to the increased cost of diesel emulsion fuel compared with current diesel
prices and the potential reduced gas mileage. Additionally, if an individual
or business decides to dispense diesel emulsion fuel, a special blending unit
will probably have to be purchased or leased. The commission estimates that
approximately 53,000 heavy-duty diesel vehicles and a portion of the 10,000
affected non-road vehicles/equipment are owned and operated by individuals
and businesses in the affected counties. These vehicles would be required
to use diesel emulsion fuel beginning May 1, 2004. Based on a 25,000 to 50,000
VMT per year the total annual cost to individuals and businesses affected
by the proposed amendments would increase by $775 to $1,550 per diesel vehicle
per year. The higher VMT was used in order to reflect the increased miles
that some privately-owned heavy-duty diesels (such as long haul semi-trucks)
accrue compared with state and local government vehicles. There will be a
cost increase associated with using diesel emulsion fuel in non-road vehicles/equipment;
however the total amount cannot be determined at this time. Total annual costs
to individuals and businesses in the affected counties, not including blending
unit and related infrastructure costs and non-road vehicles/equipment, would
be approximately $41 million to $82 million.
SMALL AND MICRO-BUSINESS ASSESSMENT
The commission determined that fiscal implications are possible as a result
of administration or enforcement of the proposed amendments, for small and
micro-businesses that own a fleet of vehicles or that dispense diesel fuel
in the HGA area. There are no known diesel fuel producers or importers that
would be considered small or micro-businesses. The commission estimates that
many independent retailers of diesel fuel, which are potential diesel emulsion
fuel retailers in the affected counties, are small or micro-businesses that
will probably not choose to mix diesel emulsion fuel on-site. The commission
anticipates that small or micro-businesses that choose to dispense diesel
emulsion fuel will purchase the mixed fuel from larger fuel distributors and
store the fuel on-site. However, if a small or micro-businesses chooses to
mix and dispense diesel emulsion fuel, a special blending unit will have to
be purchased or leased. A typical blending unit would cost approximately $400,000
installed ($350,000 for the unit and $50,000 for installation). Production
costs to produce diesel emulsion fuel, which incorporates the estimated $.08
per gallon increase based on the use of LED fuel as the baseline, are not
anticipated to affect small or micro-business except for passing increased
costs of production through to consumers. Of the 53,000 heavy-duty on-road
diesel vehicles and the 10,000 non-road vehicles/equipment affected by the
proposed amendments, some will be owned and operated by small or micro-businesses.
The total annual cost to small or micro-businesses, not including blending
unit and related infrastructure costs and non-road vehicles/equipment, would
increase by $775 to $1,550 per heavy-duty diesel vehicle per year. There will
be a cost increase associated with using diesel emulsion fuel in non-road
vehicles/equipment; however, the total amount cannot be determined at this
time. Total fiscal impact to small or micro-businesses will depend on the
total number of vehicles affected by the proposed amendments that are owned
and operated by individual small and micro-businesses.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the rulemaking in light of the regulatory impact
analysis (RIA) 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. The new sections to Chapter 114 are one element
of the HGA Attainment SIP and will require the use of diesel emulsions in
the HGA nonattainment area. While the new 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, the commission does not
believe the rules will adversely affect, in a material way, the operation
of on-road or non-road heavy- duty diesel engines or diesel emulsion fuel
distributors. 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.
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. 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 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. Thus, while specific measures are not generally required, the
emission reductions are required. 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.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code was amended by Senate Bill 633 (SB 633) during the
75th Legislative Session, 1999. The intent of SB 633 was to require agencies
to conduct a regulatory impact analysis (RIA) of extraordinary rules. These
are identified in the statutory language as 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. 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. For these reasons, rules proposed for
inclusion in the SIP fall under 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
reductions, such as those 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 obtain NO
x
emission reductions which 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 rulemaking does not exceed a standard
set by federal law, exceed an express requirement of state law (unless specifically
required by federal law), or exceed a requirement of a delegation agreement.
The rulemaking was not developed solely under the general powers of the agency,
but was specifically developed to meet the NAAQS established under federal
law and authorized under Texas Clean Air Act (TCAA), §§382.011,
382.012, 382.017, 382.019, 382.037(g), and 382.039. The commission invites
public comment on the draft regulatory impact analysis.
TAKINGS IMPACT ASSESSMENT
The commission prepared a takings impact assessment for these rules in
accordance with Texas Government Code, §2007.043. The following is a
summary of that assessment. These proposed new rules are one element of the
control strategy for the HGA Post-1999 ROP/Attainment Demonstration SIP. The
specific purpose of the rulemaking is to require on-road or non-road heavy-
duty diesel engines which are registered or primarily operated in the HGA
nonattainment area to use diesel emulsion fuel. Adoption of these requirements
to reduce NO
x
can contribute to attainment and
maintenance of the one-hour ozone standard in the HGA nonattainment area.
Promulgation and enforcement of the rules may burden private real property
because the requirement to use diesel emulsion fuel could require a diesel
emulsion fuel distributor to install a blending station or other equipment,
that could be attached to private real property. 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 fulfill federal mandates under the 42 USC, §7410. Specifically,
control requirements have been developed to meet the ozone NAAQS 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 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 this rulemaking is to implement restrictions on the use of heavy-duty on-road
and non-road engines in the HGA ozone nonattainment area to meet the 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, these proposed rules do
not constitute a takings under the Texas Government Code, Chapter 2007.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that the proposed 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.
Interested persons may submit comments on the consistency of the proposed
rules with the CMP during the public comment period.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic
Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central
Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite
200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource
Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin.
The hearings are structured for the receipt of oral or written comments by
interested persons. Registration will begin one hour prior to each hearing.
Individuals may present oral statements when called upon in order of registration.
A four-minute time limit will be established at each hearing to assure that
enough time is allowed for every interested person to speak. Open discussion
will not occur during each hearing; however, agency staff members will be
available to discuss the proposal one hour before each hearing, and will answer
questions before and after each hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend a hearing, should contact the Office of
Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Comments may be mailed to Heather Evans, Office of Environmental Policy,
Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087,
faxed to (512) 239-4808, or emailed to
siprules@tnrcc.state.tx.us
. All comments should reference Rule Log Number 2000-011K-114-AI. Comments
must be received by 5:00 p.m., September 25 2000. For further information,
please contact Sam Wells at (512) 239-1441 or Alan Henderson at (512) 239-1510.
STATUTORY AUTHORITY
The new sections are proposed 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 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 proposed 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.
The proposed new sections implement TCAA, §382.002, relating to Policy
and Purpose; §382.011, relating to General Powers and Duties; §382.012,
relating to State Air Control Plan; §382.019, relating to Methods Used
to Control and Reduce Emissions from Land Vehicles; §382.037(g), relating
to Vehicle Emissions Inspection and Maintenance Program, and §382.039,
relating to Attainment Program.
§114.330.Definitions.
Unless specifically defined in the TCAA or in the rules of the commission,
the terms used by the commission 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, 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)
Diesel emulsion additive - A type of diesel fuel additive
which allows water and diesel to be blended so that it does not separate.
The additive may also contain, but is not limited to, anti-freeze agents,
cetane enhancers, and other ingredients.
(2)
Diesel emulsion fuel - A water/fuel mixture containing
a diesel fuel additive to emulsify the water with the fuel.
(3)
Diesel emulsion fuel distributor - Any person, retailer,
jobber, bulk fuel reseller, low emission diesel refiner who distributes diesel
emulsion fuel to the ultimate user, diesel emulsion additive manufacturer,
or other entity who distributes diesel emulsion fuel required to be mixed
with a diesel emulsion additive.
(4)
Non-road heavy-duty engine - A non-road engine that is
greater than 175 nominal horsepower as rated by the manufacturer on the vehicle
nameplate and is fueled by gasoline, diesel, diesel emulsion, or any alternate
fuel, including, but not limited to, locomotives, tugs, tow-boats, construction
equipment, and ferry boats.
(5)
On-road heavy-duty diesel engine - An engine installed
in an on-road vehicle which is greater than 10,000 pounds gross vehicle weight
rating.
(6)
Primarily operated - Use of a motor vehicle or engine more
than 60 calendar days per year in an affected county. It is presumed that
an on-road vehicle is primarily operated in the county in which it is registered.
§114.331.Applicability.
The requirements of this division apply to:
(1)
diesel emulsion fuel distributors that supply fuel for
on-road heavy-duty diesel engines which are registered in the counties listed
under §114.339 (relating to Affected Counties and Compliance Dates) with
a total throughput of at least 25,000 gallons per month at one fuel dispensing
facility; and
(2)
diesel emulsion fuel distributors who supply dyed and undyed
diesel fuel for non-road heavy-duty engines primarily operated in the counties
listed under §114.339 of this title with a total throughput of at least
500 gallons per month at one fuel dispensing facility.
§114.332.Diesel Emulsion Standards.
No diesel fuel shall be used in the counties listed in §114.329
of this title (relating to Affected Counties and Compliance Dates) unless
it meets the following.
(1)
The low emission diesel fuel used to blend diesel emulsion
fuel must meet all the performance standards contained in §114.312 of
this title (regarding Low Emission Diesel Standards).
(2)
The diesel emulsion additive must be registered with the
EPA in accordance with 40 Code of Federal Regulations (CFR), Subpart 80 (concerning
Registration of Fuels and Fuel Additives, as amended on February 28, 2000).
(3)
The amount, concentration, or volume of water must be within
the diesel emulsion additive manufacturer specifications.
(4)
The diesel emulsion must:
(A)
result in emissions that are lower than the emissions of
oxides of nitrogen in the low emission diesel as follows:
(i)
on-road heavy-duty diesel engines - 15%; and
(ii)
non-road heavy-duty diesel engine - 20%; and
(B)
not result in a net increase in the other pollutant levels,
as tested in accordance with 40 CFR, Subpart 80 as amended on February 28,
2000, or Title 13, California Code of Regulations, §2281 and §2282,
as amended on June 4, 1997.
§114.336.Recordkeeping and Labeling.
(a)
All diesel emulsion fuel distributors affected by this
division shall maintain complete and accurate records for at least two years
and, upon request, shall make such records available to representatives of
the commission, EPA, or local air pollution control agency having jurisdiction
in the area. The information in the records shall include, but shall not be
limited to, proof of purchase of diesel emulsion fuel such as by bulk fuel
contract, bills of lading, purchase orders, fuel analysis, or other records
sufficient to demonstrate compliance.
(b)
All tanks in service or blending units in which diesel
emulsion fuel is stored must be clearly labeled with a sign which reads "DIESEL
EMULSION FUEL ONLY" in at least four-inch letters, and each tank must have
a visible, unique identification number which corresponds to a plot plan which
shows the location of the tank or blending unit.
§114.338.Registration.
Diesel emulsion fuel distributors must register with the executive
director. Registration will be on forms provided by the executive director
and shall include a statement of acceptance of the requirements of this division
and shall include a statement of consent by the registrant that the executive
director shall be permitted to collect samples and have access to all documentation
and records. The executive director shall maintain a listing of all registered
diesel emulsion fuel distributors.
§114.339.Affected Counties and Compliance Dates.
Beginning on May 1, 2004, the requirements of this division shall
be enforced in the counties of: Brazoria, Chambers, Fort Bend, Galveston,
Harris, Liberty, Montgomery, and Waller.
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005630
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
3.
NON-ROAD LARGE SPARK-IGNITION ENGINES
30 TAC §114.421, §114.429
The commission proposes 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 proposed in order to extend the existing requirements
for non-road, large spark-ignition engines to all counties in the state thus
controlling ground-level ozone in the state.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED 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. 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 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 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 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 approveable 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 included in
this proposal indicates a gap of an additional 77.98 tons per day (tpd) of
NO
x
reductions is necessary for an approveable
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 have formally submitted a resolution to
the commission, requesting the inclusion of many specific emission reduction
strategies.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses 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 has been made in controlling
emissions from on-road vehicles, the EPA has turned its attention to non-road
(also called off-road) engines, which also contribute significantly to air
pollution. Although emissions from non-road, large spark-ignition (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 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 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
These amendments are proposed in order to control ground-level ozone in
the state by restricting the sale and use of non-road, LSI engines 25 horsepower
(hp) and larger produced in model year 2004, and all equipment and vehicles
produced on or after January 1, 2004 that use such engines; to LSI engines
that are 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 including all future revisions 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, the 42 USC, §7543(e)(2)(B), requires
the state programs to be identical. The rules are proposed to be effective
throughout the State of Texas. The proposed 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 solicits 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.
SECTION-BY-SECTION DISCUSSION
The intent of these proposed amendments is to extend to all counties in
the State of Texas the existing non-road, LSI standards 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 cannot be reopened for public comment in this proposal because no changes
are being 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 will be §114.421 and 114.429. Section
114.421 is proposed to be amended to reflect the statewide applicability of
the LSI rules, and §114.429 is proposed to be 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 may not be reopened
because they incorporate by reference the California non-road, LSI rules and
all future revisions 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 proposal
makes 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 proposed amendments extend the
control requirements to all counties within the state. Proposed §114.429
also specifies the compliance schedule for engine manufacturers.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT
John Davis, Technical Specialist with Strategic Planning and Appropriations,
determined that for the first five-year period the proposed amendments to
Chapter 114 are in effect there will be no significant fiscal implications
for any single unit of state and local government as a result of administration
or enforcement of the proposed amendments unless that unit of government replaces
between 200 and 1,000 of these engines annually. The proposed amendments to
Chapter 114 would require units of state and local government, businesses,
and individuals statewide that own or operate non-road LSI engines of 25 hp
and larger produced on or after January 1, 2004, and all equipment and vehicles
produced on or after January 1, 2004 that use such engines, to use LSI engines
certified under 13 CCR 9 as adopted by the CARB on October 19, 1999.
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 technologies to reduce emissions. The CARB has determined
the proposed standards are technologically feasible and has adopted exhaust
emission standards for these engines designed to reduce NO
x
and VOC emissions. Oxides of nitrogen and VOC are precursor chemicals
that contribute to the production of ground-level ozone.
The proposed amendments include exemptions for: 1.) Engines less than 175
hp used in construction and agriculture; 2.) Engines operated on or in any
device used exclusively upon stationary rails or tracks; 3.) Engines used
to propel marine vessels; 4.) Internal combustion engines attached to a foundation
at a location for at least 12 consecutive months; 5.) Recreational vehicles
and snowmobiles; and 6.) Stationary or transportable gas turbines for power
generation.
The commission is required to submit a new SIP revision by the end of 2000
which will bring the HGA nonattainment area into attainment with the ozone
NAAQS by 2007. The rule proposed for the HGA nonattainment area in this notice
is one element of the HGA Post-1999 ROP/Attainment Demonstration SIP. A SIP
is a plan developed for any region where existing (measured and/or modeled)
ambient levels of pollutants exceed the levels specified in a national standard.
The plan sets forth a control strategy that provides emission reductions necessary
for attainment and maintenance of the national standards. The proposed set
of rules are necessary for the HGA nonattainment area to be able to demonstrate
attainment with the ozone NAAQS.
The cost of the technology needed to reduce emissions from these engines
to comply with the standards is projected by an environmental consultant (Environ)
to be approximately $100 to $500 per engine depending upon the engine size
and typical engine type. Engines that currently apply closed- loop control
would require less additional equipment reducing the overall cost of meeting
the new standard. The commission estimated that the total cost impact of reducing
emissions from the 176,522 engines to be purchased during calendar years 2004
through 2007 will be in the range of $18 million to $88 million or an average
of approximately $4 million to $22 million per year from 2004 through 2007.
A breakdown of the total number of engines bought by owner (i.e. state and
local government, individuals or businesses) is not available at this time.
However, the costs are not anticipated to be significant to any single unit
of state or local government, unless that unit of government replaces between
200 and 1,000 of these engines annually.
PUBLIC BENEFIT AND COSTS
Mr. Davis also determined that for each year of the first five years the
proposed amendments to Chapter 114 are in effect, the public benefit anticipated
from enforcement of and compliance with the proposed amendments will be the
potential reduction of NO
x
and VOC emissions,
potentially improved air quality, and contribution toward demonstration of
attainment with the ozone NAAQS.
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
the proposed amendments unless an entity replaces between 200 and 1,000 of
these engines annually. The proposed amendments to Chapter 114 would require
units of state and local government, businesses, and individuals statewide
that own or operate non-road LSI engines of 25 hp and larger produced on or
after January 1, 2004, and all equipment and vehicles produced on or after
January 1, 2004 that use such engines to use LSI engines certified under 13
CCR 9 as adopted by the CARB on October 19, 1999. Affected owners and operators
of this equipment will not be required to retrofit or purchase new engines
for their existing inventory. However, if equipment is replaced with equipment
produced after January 1, 2004, the new equipment must meet the proposed standards.
The proposed amendments allow manufacturers to continue to sell in-stock
equipment that predates the proposed amendments in a phase-down manner. The
phase-down requires that 25% of the equipment sold in year 2004 must have
CARB-certified engines; 50% in year 2005; and 100% in year 2006 and thereafter.
It is estimated that 25% of the engines sold in year 2004 will be CARB-certified
engines that meet the proposed standards. The commission also estimated that
50% of the engines sold in year 2005 will be CARB-certified engines. In years
2006 and thereafter, the commission estimated that all engines sold will be
CARB-certified engines. The commission estimated that 12,089 CARB- certified
engines will be purchased statewide during year 2004; 27,098 certified engines
in year 2005; 65,189 certified engines in 2006; and 72,146 certified engines
in 2007, for a total of 176,522 CARB- certified engines during calendar years
2004 through 2007.
The cost of the technology needed to reduce emissions from these engines
to comply with the standards is projected by an environmental consultant (Environ)
to be approximately $100 to $500 per engine depending upon the engine size
and typical engine type. Engines that currently apply closed- loop control
would require less additional equipment reducing the overall cost of meeting
the new standard. It is estimated that the total cost impact of reducing emissions
from the 176,522 engines projected to be purchased during calendar years 2004
through 2007 will be in the range of $18 million to $88 million or an average
of approximately $4 million to $22 million per year from 2004 through 2007.
These costs may be mitigated by improved performance of these types of
engines. 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."
SMALL AND MICRO-BUSINESS ASSESSMENT
There are no significant fiscal implications anticipated to small and micro-businesses
as a result of implementing the proposed amendments because there are no known
small or micro-businesses that would need to replace from 200 to 1,000 of
these engines annually. Estimates of the number of small and micro-businesses
statewide that own and operate non-road equipment powered by LSI engines of
25 hp and larger are not available at this time; however, it is anticipated
that costs would be similar to those for business in general as indicated
in the Public Benefit and Costs Section of this preamble. The cost of the
technology needed to reduce emissions from these engines to comply with the
standards is projected by an environmental consultant (Environ) to be approximately
$100 to $500 per engine depending upon the engine size and typical engine
type. Engines that currently apply closed-loop control would require less
additional equipment reducing the overall cost of meeting the new standard.
The costs will depend less on the relative size of the company, and more on
the size and number of non-road equipment powered by LSI engines that they
own and operate.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the proposed rulemaking 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. The new sections to Chapter 114 are one element of the HGA attainment
SIP. While the new 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 this preamble, the commission does not believe
the rules will adversely affect, in a material way, the sale or use of non-road
large spark-ignition (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.
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. 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 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. Thus, while specific measures are not generally required, the
emission reductions are required. 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.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code was amended by Senate Bill 633 (SB 633) during the
75th Legislative Session, 1999. The intent of SB 633 was to require agencies
to conduct a regulatory impact analysis (RIA) of extraordinary rules. These
are identified in the statutory language as 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. 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. For these reasons, rules proposed for
inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a),
because they are required by federal law.
The proposed 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 proposed 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.
This air pollution control program is part of the strategy to reduce emissions
of NO
x
necessary for the counties included in
the HGA nonattainment area to be able to demonstrate attainment with the ozone
NAAQS. The commission is required to submit a new SIP revision by the end
of 2000 which will bring the HGA nonattainment area into attainment by 2007.
The rules proposed for HGA nonattainment area in this notice is one element
of the ozone attainment demonstration SIP for HGA. The proposed set of rules
are necessary for the HGA nonattainment area to be able to demonstrate attainment
with the ozone NAAQS. In addition, §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 proposal is not an express requirement of state law. This proposal
is intended to help bring ozone nonattainment areas into compliance, and to
help keep attainment and near nonattainment areas from becoming nonattainment
areas. The proposed amendments do not exceed a standard set by federal law,
exceed an express requirement of state law unless specifically required by
federal law, nor exceed a requirement of a delegation agreement. The proposed
amendments were not developed solely under the general powers of the agency
but were specifically developed to meet the air quality standards established
under federal law as NAAQS, as authorized under Texas Clean Air Act (TCAA), §§382.012,
382.017, 382.019, and 382.039.
The commission invites public comment on the draft regulatory impact analysis.
TAKINGS IMPACT ASSESSMENT
The commission has prepared a takings impact assessment for these rules
in accordance with Texas Government Code, §2007.043. The following is
a summary of that assessment. The specific purpose of the rulemaking is 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 proposed rulemaking 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 the proposed rules will not burden private, real property.
Although the proposed 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 this proposal 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 the rule proposal 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 proposed rules is that of an action reasonably taken to fulfill
an obligation mandated by federal law. Therefore, these proposed revisions
will not constitute a taking under the Texas Government Code, Chapter 2007.
COASTAL MANAGEMENT PROGRAM CONSISTENCY REVIEW
The commission determined that the proposed 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 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.
Interested persons may submit comments on the consistency of the proposed
rules with the CMP during the public comment period.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic
Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central
Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite
200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource
Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin.
The hearings are structured for the receipt of oral or written comments by
interested persons. Registration will begin one hour prior to each hearing.
Individuals may present oral statements when called upon in order of registration.
A four-minute time limit will be established at each hearing to assure that
enough time is allowed for every interested person to speak. Open discussion
will not occur during each hearing; however, agency staff members will be
available to discuss the proposal one hour before each hearing, and will answer
questions before and after each hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend a hearing, should contact the Office of
Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087,
faxed to (512) 239- 4808, or emailed to
siprules@tnrcc.state.tx.us
. All comments should reference Rule Log Number 2000-011G-114-AI. Comments
must be received by 5:00 p.m., September 25, 2000. For further information,
please contact Roland Castaneda, II at (512) 239-0774, or Alan Henderson at
(512) 239-1510.
STATUTORY AUTHORITY
The amendments are proposed 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 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 proposed 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.
The proposed amendments implement TCAA, §382.002, relating to Policy
and Purpose; §382.011, relating to General Powers and Duties; §382.012,
relating to State Air Control Plan; §382.019, relating to Methods Used
to Control and Reduce Emissions from Land Vehicles; and §382.039, relating
to Attainment Program.
§114.421.Emission Specifications.
(a)
(No change.)
(b)
Exhaust emissions from new non-road, LSI engines manufactured
for sale, sold, or offered for sale, or that are introduced, delivered or
imported for introduction into commerce in the
State of Texas
[
(c)
New non-road, LSI engines operated in the
State of
Texas
[
(d)
(No change.)
§114.429.Affected Counties and Compliance Schedules.
[
The provisions of this division
shall apply in the following counties: Collin, Dallas, Denton, Ellis, Johnson,
Kaufman, Parker, Rockwall, and Tarrant Counties.]
(a)
[
(b)
[
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005645
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
30 TAC §§114.440 - 114.442, 114.445, 114.446, 114.448, 114.449
The Texas Natural Resource Conservation Commission (commission)
proposes new §114.440, Definitions; §114.441, Applicability; §114.442,
Control Requirements; §114.445, Emission Reduction Credits; §114.446,
Recordkeeping and Labeling; §114.448; Registration; and §114.449;
Affected Counties and Compliance Dates. The commission proposes these amendments
to Chapter 114, Control of Air Pollution From Motor Vehicles; Subchapter I,
Non-road Engines; new Division 5, Nitrogen Oxides Reduction Systems; and corresponding
revisions to the state implementation plan (SIP) in order to control ground-level
ozone in the Houston/Galveston (HGA) ozone nonattainment area.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED 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. 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 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 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 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 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 included in
this proposal indicates a gap of an additional 77.98 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 16.25 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.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses in support of the HGA ozone attainment demonstration. In
addition, this SIP contains Post- 1999 ROP plans for the milestone years 2002,
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 proposed amendments are one element of the control strategy for the
HGA Post-1999 ROP/Attainment Demonstration SIP. The proposed amendments would
require owners or operators of on-road or non-road vehicles or equipment manufactured
prior to model year 1997 having a heavy-duty on-road or non-road engine and
fueled by gasoline, diesel, diesel emulsion fuel or any alternate fuel located
in Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery,
and Waller Counties to use exhaust systems that will achieve a 80% reduction
in NO
x
emissions from what the engine would emit
without the exhaust system. Examples of exhaust systems that could be used
to meet the proposed rule are NO
x
adsorbers,
methane catalysts, diesel oxidation catalysts, selective catalyst reduction,
lean NO
x
catalysts, and other exhaust after-treatment
systems. Adoption of these requirements to reduce NO
x
can contribute to attainment and maintenance of the one-hour ozone
standard in the HGA area.
The commission solicits 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 systems 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.
SECTION BY SECTION DISCUSSION
The proposed §114.440 has the following definitions: "NO
x
Reduction System" is defined as an exhaust or engine-related control
device designed for gasoline or diesel engine exhaust systems to achieve NO
Proposed §114.441 provides that owners or operators of on-road or
non-road vehicles or equipment manufactured prior to model year 1997 having
a heavy-duty on-road or non-road engine and fueled by gasoline, diesel, diesel
emulsion fuel, or any alternate fuel primarily operated in Brazoria, Chambers,
Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties must
comply with the requirements of Subchapter I, Division 5. The commission believes
these model years are appropriate because newer vehicles and engines have
generally much lower NO
x
emissions. Thus, the
commission believes the regulatory focus should be on the older heavy-duty
engines with higher emissions.
Proposed §114.442 provide the criteria for use of heavy-duty on-road
and non-road engines in the affected counties. NO
x
reduction systems used by any heavy-duty on-road and non-road engines in the
affected counties must, at a minimum, comply with the emissions testing and
emission standards required by applicable EPA or California Air Resources
Board (CARB) regulations. The NO
x
reduction system
installed on the vehicle or engine must be able to reduce NO
x
emissions by at least 80%. Initial laboratory tests show that the
use of NO
x
reduction systems can reduce NO
The commission anticipates that NO
x
reduction
systems currently under development will be available by May 1, 2004, the
proposed compliance date for the proposed rules. The commission believes this
is true because NO
x
reduction systems are being
developed. However, the commission acknowledges that no NO
x
reduction systems have been certified for use by the EPA in on-road
and non-road applications. This is because most of these systems are used
in large, stationary, industrial diesels which have steady-state loads. Nevertheless,
the commission believes that these systems will be developed and that they
are critical towards obtaining necessary reductions in NO
x
emissions in the HGA nonattainment area. Further, to provide consistency
in the development process and for implementation, it is important that these
systems be able to meet applicable EPA and CARB standards. However, heavy-
duty on-road and non-road engines are often subjected to harsh, transient
loads which cause variation in catalyst performance. For these reasons, the
commission is specifically soliciting comments about alternatives to the use
of NO
x
reduction systems as means of control
which could achieve the same emission reductions.
Proposed §114.445 provides the incentive for owners or operators of
affected heavy-duty on-road and non-road engines to install NO
x
reduction systems that result in reductions in excess of the required
80% NO
x
emissions reduction. If a NO
x
reduction system is used that will achieve greater than 80% NO
Recordkeeping and labeling requirements are addressed in proposed §114.446.
The owner or operator of heavy-duty on-road and non-road engines in the affected
counties must follow manufacturer installation, maintenance, and labeling
requirements as required for the NO
x
reduction
system and by the EPA in 40 Code of Federal Regulations (CFR) Part 86, Control
of Emissions from New and In-Use Highway Vehicles and Engines as amended on
February 28, 2000; or 40 CFR Part 89, Control of Emissions from New and In-Use
Nonroad Compression-Ignition Engines; or by CARB in Title 13, California Code
of Regulations, §1976, as amended on February 26, 1999.
Registration of on-road and non-road engines is specified in §114.448.
Owners and operators of affected engines must register using a form available
from the executive director which proves that a NO
x
reduction system that meets the requirements of Chapter 114 was properly
installed.
Affected counties are addressed in §114.449. The affected counties
in the HGA ozone nonattainment area are Brazoria, Chambers, Fort Bend, Galveston,
Harris, Liberty, Montgomery, and Waller. If adopted, compliance with the rules
would be required on May 1, 2004.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT
John Davis, Technical Specialist with Strategic Planning and Appropriations,
has determined that for the first five-year period the proposed amendments
are in effect, there will be fiscal implications which may be significant
for units of state and local government located in the HGA ozone nonattainment
area as a result of administration or enforcement of the proposed amendments.
The proposed amendments require the use of NO
x
reduction systems, that will achieve a 80% reduction in NO
x
, from all engines manufactured prior to model year 1997 installed
in on-road vehicles with a GVWR greater than 10,000 pounds and on engines
rated at 175 nominal hp or greater used in non-road locomotives and commercial
marine vessels primarily operated in the HGA ozone nonattainment area by May
1, 2004. The NO
x
reductions must be accomplished
without increasing other pollutants. The HGA area consists of Brazoria, Chambers,
Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller counties. The
proposed rules would affect approximately 340 state and local government and
64,000 privately owned and operated on-road heavy-duty vehicles and an unknown
number of locomotives and commercial marine vessels.
Examples of NO
x
reduction systems that could
be used to meet the proposed rules are NO
x
absorbers,
methane catalysts, diesel oxidation catalyst, selective catalyst reduction,
lean NO
x
catalysts, and other exhaust after-treatment
systems.
The commission anticipates that approximately 340 heavy-duty on-road vehicles
are owned and operated by state and local governments. Based on a report from
the Manufacturers of Emission Controls Association (MECA) titled
Emission Control Retrofit of Diesel-Fueled Vehicles
, the cost to state
and local governments to purchase emission control devices that would meet
the emission requirements of the proposed amendments would range from $500
to $2,000 per heavy-duty on-road and non-road vehicles/equipment.
The total costs to state and local governments within the HGA area would
be approximately $170,000 to $680,000 for heavy-duty on-road vehicles/equipment
as a result of implementing the proposed amendments. The total costs do not
factor in non-road locomotives and commercial marine vessels because the total
number owned and operated by state and local governments in the HGA area is
unknown. The commission anticipates the operating costs associated with the
proposed amendments will not be significant unless 50 - 200 or more affected
vehicles/equipment are owned and operated by a single unit of state or local
government.
PUBLIC BENEFIT AND COSTS
Mr. Davis also has determined that for the first five years the proposed
amendments are in effect, the public benefit anticipated from enforcement
of and compliance with the proposed amendments will be the potential reduction
of on-road and non-road mobile source emissions, potentially improved air
quality, and contribution toward demonstration of attainment with the NAAQS
for the HGA ozone nonattainment areas.
The proposed amendments require the use of NO
x
reduction systems that will achieve an 80% reduction in NO
x
, from all engines manufactured prior to model year 1997 installed
in on-road vehicles with a GVWR greater than 10,000 pounds and engines rated
at 175 nominal hp or greater installed in non-road locomotives and commercial
marine vessels primarily operated in the HGA area by May 1, 2004. The NO
The commission estimates that approximately 64,000 heavy-duty on-road vehicles
affected by the proposed amendments are owned and operated by individuals
and businesses. Based on a report from the MECA titled
Emission Control Retrofit of Diesel-Fueled Vehicles
, the cost to state
and local governments to purchase emission control devices that would meet
the emission requirements of the proposed amendments would range from $500
to $2,000.
The total costs to individuals and businesses within the HGA area as a
result of the proposed amendments would be approximately $32 million to $128
million as a result of implementing the proposed amendments. The total costs
does not factor in non-road locomotives or commercial marine vessels because
the total number owned and operated by individuals and businesses in the HGA
area is unknown. The total fiscal impact to individuals and businesses would
depend on the number of vehicles that would be required to have the NO
SMALL AND MICRO-BUSINESS ASSESSMENT
There may be adverse fiscal implications for small or micro-businesses
located in the HGA area as a result of administration or enforcement of the
proposed amendments. The proposed amendments require the use of NO
x
reduction systems that will achieve a 80% reduction in NO
x
, on all engines manufactured prior to model year 1997 installed in
on-road heavy-duty vehicles with a GVWR greater than 10,000 pounds or higher,
and engines with a hp rating greater than 175 installed in non-road locomotives
and commercial marine vessels primarily operated in the HGA area by May 1,
2004. The NO
x
reductions must be accomplished
without increasing other pollutants. Of the approximately 64,000 privately
owned and operated on-road heavy- duty vehicles and the unknown number of
non-road locomotives and commercial marine vessels affected by the proposed
amendments, some are anticipated to be owned and operated by small and/or
micro-businesses in an amount that cannot be determined. The cost to small
or micro-businesses to purchase emission control devices that would meet the
emission requirements of the proposed amendments would range from $500 to
$2,000 per vehicle affected by the proposed amendment. The total fiscal impact
to small or micro-businesses would depend on the number of vehicles that would
be required to have the NO
x
reduction systems
installed.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the rulemaking in light of the regulatory analysis
requirements of Texas Government Code, §2001.0225, and has 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. The amendments to Chapter 114 are one element of the HGA Post-
1999 ROP/Attainment Demonstration SIP and will require NO
x
emission reductions from owners or operators of heavy-duty on-road
and non-road engines in the HGA ozone nonattainment area. The commission does
not believe the rules will have an adverse, material affect or will impact
a sector of the economy. While the new 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, the commission does not believe the
rules will adversely affect, in a material way, the use of heavy-duty engines
greater than 10,000 pounds GVWR or heavy-duty non-road engines that are greater
than 175 nominal hp as rated by the manufacturer on the nameplate, both of
which are fueled by gasoline, diesel, diesel emulsion fuel, or any alternative
fuel. The commission does not believe that the owners or operators of 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.
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 §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 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 42 USC 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. 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. Thus, while specific measures are not generally required, the
emission reductions are required. 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.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code was amended by Senate Bill (SB) 633 during the 75th
Legislative Session. The intent of SB 633 was to require agencies to conduct
a regulatory impact analysis (RIA) of extraordinary rules. These are identified
in the statutory language as 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. 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 42 USC. For these reasons, rules proposed for
inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a),
because they are required by federal law. 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. This rulemaking action
does not exceed an express requirement of state law. This rulemaking action
is intended to obtain NO
x
emission reductions
which 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 rulemaking does not exceed a standard
set by federal law, exceed an express requirement of state law (unless specifically
required by federal law), or exceed a requirement of a delegation agreement.
The rulemaking was not developed solely under the general powers of the agency,
but was specifically developed to meet the NAAQS established under federal
law and authorized under Texas Clean Air Act (TCAA) §§382.002, 382.011,
382.012, 382.019, and 382.039.
The commission invites public comment on the draft regulatory impact analysis
determination.
TAKINGS IMPACT ASSESSMENT
The commission prepared a takings impact assessment for these rules in
accordance with Texas Government Code, §2007.043. The following is a
summary of that assessment. These proposed new sections are one element of
the control strategy for the HGA Post-1999 ROP/Attainment Demonstration SIP.
The specific purpose of the rulemaking is to require owners or operators of
on- road or non-road vehicles or equipment manufactured prior to model year
1997 having a heavy-duty on-road or non-road engine and fueled by gasoline,
diesel, diesel emulsion fuel, or any alternate fuel located in the HGA nonattainment
area to use exhaust systems that will achieve a 80% reduction in NO
x
emissions from what the engine would emit without the exhaust technology.
Adoption of these requirements to reduce NO
x
can contribute to attainment and maintenance of the one-hour ozone standard
in the HGA area.
Promulgation and enforcement of the rule amendments will not burden private
real property because the NO
x
reduction system
requirement applies to heavy-duty on-road and non-road engines, which are
not attached to, or considered to be, private real property. 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 fulfill federal mandates under the 42 USC, §7410.
Specifically, control requirements have been developed to meet the ozone NAAQS
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 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 this rulemaking action is to implement restrictions
on the use of heavy-duty on-road and non-road engines in the HGA ozone nonattainment
area to meet the 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,
these proposed rules do not constitute a takings under the Texas Government
Code, Chapter 2007.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that this 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 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 action for consistency with the CMP goals
and policies in accordance with the regulations of the Coastal Coordination
Council. For this rulemaking, the commission determined that the 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. This rulemaking will require owners
or operators of on-road or non-road vehicles or equipment manufactured prior
to model year 1997 having a heavy-duty on-road or non-road engine and fueled
by gasoline, diesel, diesel emulsion fuel, or any alternate fuel located in
the HGA nonattainment area to use exhaust systems that will achieve a 80%
reduction in NO
x
emissions from what the engine
would emit without the exhaust system. Adoption of these requirements to reduce
NO
x
can contribute to attainment and maintenance
of the one-hour ozone standard in the HGA area. This action is consistent
with the CMP because it does not authorize any new emissions and will reduce
existing emissions of NO
x
.
Interested persons may submit comments on the consistency of the proposed
rules with the CMP during the public comment period.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic
Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central
Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite
200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource
Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin.
The hearings are structured for the receipt of oral or written comments by
interested persons. Registration will begin one hour prior to each hearing.
Individuals may present oral statements when called upon in order of registration.
A four-minute time limit will be established at each hearing to assure that
enough time is allowed for every interested person to speak. Open discussion
will not occur during each hearing; however, agency staff members will be
available to discuss the proposal one hour before each hearing, and will answer
questions before and after each hearing.
Persons with disabilities who have special communication or other accommodation
needs who are planning to attend the hearing should contact the Office of
Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, faxed to (512) 239-4808,
or emailed to
siprules@tnrcc.state.tx.us
.
All comments should reference Rule Log Number 2000- 011M-114-AI. Comments
must be received by 5:00 p.m., September 25, 2000. For further information,
please contact Sam Wells at (512) 239-1441 or Alan Henderson at (512) 239-1510.
STATUTORY AUTHORITY
The new sections are proposed under the 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 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 new sections are also proposed
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.
The proposed new sections implement TCAA, §382.002, relating to Policy
and Purpose; §382.011, relating to General Powers and Duties; §382.012,
relating to State Air Control Plan; §382.019, relating to Methods Used
to Control and Reduce Emissions from Land Vehicles; and §382.039, relating
to Attainment Program.
§114.440.Definitions.
Unless specifically defined in the TCAA or in the rules of the commission,
the terms used by the commission 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, the following words and terms, when used in this chapter,
shall have the following meanings, unless the context clearly indicates otherwise.
(1)
Heavy-duty on-road engine - An on-road engine installed
in an on-road vehicle that is greater than 10,000 pounds gross vehicle weight
rating, and is fueled by gasoline, diesel, diesel emulsion fuel, or any alternate
fuel.
(2)
Heavy-duty non-road engine - A non-road engine used in
locomotives, tugs, tow-boats, and ferry boats that is greater than 175 nominal
horsepower as rated by the manufacturer on the vehicle nameplate and is fueled
by gasoline, diesel, diesel emulsion, or any alternate fuel.
(3)
Nitrogen oxides (NO
x
) reduction
system - An exhaust or engine-related control device designed for gasoline
or diesel engine exhaust systems to achieve NO
x
emissions reductions;
(4)
Primarily operated - Use of a motor vehicle or engine more
than 60 calendar days per year in an affected county. It is presumed that
an on-road vehicle is primarily operated in the county in which it is registered.
§114.441.Applicability.
(a)
Owners or operators of non-road vehicles or equipment manufactured
prior to model year 1997 having a heavy-duty non-road engine primarily operated
in the counties listed in §114.449 of this title (relating to Affected
Counties and Compliance Dates) must comply with the requirements of this division.
(b)
Owners or operators of on-road vehicles or equipment manufactured
prior to model year 1997 having a heavy-duty on-road engine primarily operated
in the counties listed in §114.449 of this title must comply with the
requirements of this division.
§114.442.Control Requirements.
(a)
Non-road vehicles or equipment manufactured prior to model
year 1997 using heavy-duty on-road and non-road engines primarily operated
in the counties listed in §114.449 of this title (relating to Affected
Counties and Compliance Dates) must use nitrogen oxides (NO
x
) emission reduction systems that are approved:
(1)
by the EPA as to their emissions as tested by the applicable
Federal Test Procedure in 40 Code of Federal Regulations (CFR) Part 86, Control
of Emissions from New and In-Use Highway Vehicles and Engines as amended on
February 28, 2000; or 40 CFR Part 89, Control of Emissions from New and In-Use
Nonroad Compression-Ignition Engines as amended on October 23, 1998; or
(2)
by the California Air Resources Board as tested by the
applicable emissions test in Title 13, California Code of Regulations, §1976,
as amended on February 26, 1999.
(b)
Owners or operators of heavy-duty engines subject to §114.441
of this title (relating to Applicability) shall ensure that the NO
x
reduction system has a minimum control efficiency of 80% for NO
(c)
The installation of the NO
x
reduction system cannot result in an increase in any pollutant.
§114.445.Emission Reduction Credits.
(a)
Owners or operators of heavy-duty engines subject to §114.441
of this title (relating to Applicability) that install nitrogen oxides (NO
(b)
In order to demonstrate that the NO
x
reduction system will achieve emission reductions of greater than
80%, the owner or operator of the on-road heavy-duty engine or non-road heavy-duty
engine must demonstrate that all applicable sections of this chapter are met,
including the following provisions:
(1)
§114.20 of this title (relating to Maintenance and
Operation of Air Pollution Control Systems or Devices Used to Control Emissions
from Motor Vehicles);
(2)
§§114.150-157 of this title (relating to Requirements
for Mass Transit Authorities, Requirements for Local Governments and Private
Entities, Exceptions, Exceptions for Certain Mass Transit Authorities, Reporting,
Record Keeping, and Low Emission Vehicle Fleet Program Compliance Credits);
and
(3)
the requirements of Chapter 114, Control of Air Pollution
from Motor Vehicles, Subchapter I, Non-Road Engines, Division 5: Airport Ground
Support Equipment; Division 2: Heavy Equipment Fleets - Compression-Ignition
Engines; Division 3: Non-Road Large Spark-Ignition Engines; and Division 4:
Construction Equipment Operating Restrictions.
§114.446.Recordkeeping and Labeling.
Owners or operators of heavy-duty on-road and non-road engines subject
to §114.441 of this title (relating to Applicability) that install nitrogen
oxides (NO
x
) reduction systems must follow all:
(1)
written procedures by the manufacturer of the NO
x
reduction systems, as to engine maintenance and recordkeeping; and
(2)
written labeling requirements set by the EPA in 40 Code
of Federal Regulations (CFR), Part 86, as amended on February 28, 2000 or
the California Air Resources Board in Title 13, California Code of Regulations, §1976,
as amended on February 26, 1999.
§114.448.Registration.
Owners or operators of heavy-duty on-road and non-road engines subject
to §114.441 of this title (relating to Applicability) that install nitrogen
oxides (NO
x
) reduction systems must submit registration
on an appropriate form available from the executive director which will require
information that demonstrates compliance with the requirements of this division.
§114.449.Affected Counties and Compliance Dates.
Beginning on May 1, 2004, the requirements of this division shall be
enforced in the following counties: Brazoria, Chambers, Fort Bend, Galveston,
Harris, Liberty, Montgomery, and Waller.
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005629
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
30 TAC §114.452, §114.459
The Texas Natural Resource Conservation Commission (commission)
proposes new §114.452, Control Requirements, and §114.459, Affected
Counties and Compliance Dates. The commission proposes 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 proposes
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 proposed revisions are one element of the control strategy for the
proposed HGA Post-1996 Rate-of-Progress (ROP)/Attainment Demonstration SIP.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED 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. 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. 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 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 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,
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 included in
this proposal indicates a gap of an additional 77.98 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 0.58 tpd delay of NO
x
until
after noon. There will also be a 20.6 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 7.7 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, 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.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses 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 proposed rules is to establish a restriction on the
use of handheld and non-handheld spark-ignition lawn and garden service equipment
that operate at or below 25 horsepower (hp), 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 counties included in the HGA nonattainment
area to be able to demonstrate attainment with the NAAQS for ozone.
The proposed revisions would implement an operating-use restriction program
requiring that the handheld and non-handheld spark-ignition lawn and garden
service equipment, rated at 25-hp and below, be restricted from use 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, chainsaws,
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 eight-county HGA nonattainment
area of Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery,
and Waller Counties. The effective date would be April 1, 2005.
The intent of these proposed 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. Between these hours
this equipment is restricted from operating. 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 proposed rules.
That is, electric or man-powered lawn equipment may be utilized. It should
be noted however that the regulated types of lawn and garden service equipment
are banned from use during the hours specified regardless of how they are
being used.
The amount of NO
x
shifted will total 0.58
tpd. The non-road mobile source category is one of the few sources of ozone-causing
emissions that are not currently regulated. Federal controls on handheld lawn
and garden service equipment such as cleaner-burning engines have been adopted,
and will be phased in beginning with the 2002 model year.
The California Air Resources Board (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." 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 lawn and garden equipment will not mix in the
atmosphere with other ozone-causing compounds until later in the day. 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 VOC is early in
the day. By delaying the release of NO
x
emissions
from lawn and garden service equipment until later in the day, production
of ozone will be stalled until optimum conditions no longer exist, thus avoiding
the production of higher levels of ozone.
The commission solicits 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 is soliciting 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 10th 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 proposed regarding lawn and garden service equipment
operating restrictions.
The proposed new §114.452 establishes control requirements for lawn
and garden service equipment operating-use limitations. The proposal restricts
the operation by all persons of all handheld or non-handheld lawn and garden
service 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.
The proposed new §114.459 specifies the counties which are subject
to the new requirements. The affected counties include all counties in the
HGA nonattainment area, including Brazoria, Chambers, Fort Bend, Galveston,
Harris, Liberty, Montgomery, and Waller Counties.
FISCAL NOTE AND COSTS TO STATE AND LOCAL GOVERNMENTS
John Davis, Technical Specialist with Strategic Planning and Appropriations,
has determined that for the first five-year period the proposed rules are
in effect, there will be fiscal implications which are not anticipated to
be significant for units of state and local government as a result of administration
or enforcement of the proposed rules.
The proposed rules would restrict the use of handheld and non-handheld
spark-ignition lawn and garden equipment, rated at 25 hp or less, from use
between the hours of 6:00 a.m. and noon, from April 1 through October 31.
The restriction would apply to lawn and garden equipment in the eight-county
HGA ozone nonattainment area. The proposed rules would become effective April
1, 2005. The proposed rules do not require additional control equipment or
new emission control technologies to be applied to the affected lawn and garden
equipment.
The commission is required to submit a new SIP revision by the end of 2000
which will bring the HGA into attainment by 2007. The rules proposed for HGA
in this notice comprise one element of the ozone Attainment Demonstration
SIP for HGA. The purpose of the proposed rules is for the HGA nonattainment
area to demonstrate attainment with the ozone NAAQS. The plan sets forth a
control strategy that provides emission reductions necessary for attainment
and maintenance of the national standards.
The commission estimates that units of state and local government within
the HGA ozone nonattainment area may have to pay more to contract for landscape
services if landscape businesses charge more for their services due to the
proposed time restrictions. Although the extent of the fiscal implications
are not known at this time, the commission anticipates that the potential
increased costs to units of state and local government as a result of the
proposed rules will not be significant.
PUBLIC BENEFIT AND COSTS
Mr. Davis also determined that for each year of the first five years the
proposed rules are in effect, the public benefit anticipated from enforcement
of and compliance with the proposed rules will be a potential reduction in
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, potentially improved air quality,
and contribution toward demonstration of attainment with the NAAQS for ozone.
The proposed rules would restrict the use of handheld and non-handheld
spark-ignition lawn and garden equipment, rated at 25 hp or less, from use
between the hours of 6:00 a.m. and noon, from April 1 through October 31.
The restriction would apply to lawn and garden equipment in the HGA ozone
nonattainment area. The proposed rules would become effective April 1, 2005.
The proposed rules do not require additional control equipment or new emission
control technologies to be applied to the affected lawn and garden equipment.
Persons within the HGA ozone nonattainment area that utilize equipment
affected by the proposed rules may experience adverse fiscal implications
in an amount that cannot be determined at this time. Because the proposed
rules do not require additional control equipment or new technology, the commission
does not anticipate significant economic impacts to commercial operators beyond
the shift in work schedule and possible implications caused by potential work
delays attributable to the proposed rules. Delaying use of lawn and garden
equipment until after noon may require commercial operators to adjust their
work schedules and could cause extensions of projects or the need to hire
more employees and procure additional equipment to meet business requirements.
Private operators that utilize commercial operators to perform lawn and garden
related work may have to pay more for the services.
SMALL BUSINESS AND MICRO-BUSINESS ASSESSMENT
There will be fiscal implications, in an amount which cannot be determined,
which may have an adverse fiscal impact on small or micro-businesses as a
result of administration or enforcement of the proposed rules.
The proposed rules would restrict the use of handheld and non-handheld
spark-ignition lawn and garden equipment, rated at 25 hp or less, from use
between the hours of 6:00 a.m. and noon, from April 1 through October 31.
The restriction would apply to lawn and garden equipment in the HGA ozone
nonattainment area. The proposed rules would become effective April 1, 2005.
The proposed rules do not require additional control equipment or new emission
control technologies to be applied to the affected lawn and garden equipment.
Small or micro-businesses within the HGA ozone nonattainment area that
utilize equipment affected by the proposed rules may experience adverse fiscal
implications in an amount that cannot be determined at this time. Because
the proposed rules do not require additional control equipment or new technology,
the commission does not anticipate significant economic impacts to affected
individuals and businesses beyond the shift in work schedule and possible
implications caused by potential work delays attributable to the proposed
amendments. Delaying use of lawn and garden equipment until after noon may
require affected small or micro-businesses to adjust their work schedules
and could cause extensions of projects or the need to hire more employees
and procure additional equipment to meet business requirements. Small or micro-businesses
that utilize businesses to perform lawn and garden related work may have to
pay more for the services.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the proposed rulemaking 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. The proposed rules to 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 are available at this time, the commission
does not believe work delays could affect a sector of the economy in a material
way. The proposed rules are intended to implement an operating-use restriction
program requiring that certain lawn and garden equipment 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.
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. 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 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. Thus, while specific measures are not generally required, the
emission reductions are required. 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.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code was amended by Senate Bill 633 (SB 633) during the
75th Legislative Session, 1999. The intent of SB 633 was to require agencies
to conduct a regulatory impact analysis (RIA) of extraordinary rules. These
are identified in the statutory language as 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. 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. For these reasons, rules proposed for
inclusion in the SIP fall under 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
reductions, such as those 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 obtain NO
x
emission reductions which 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 rulemaking does not exceed a standard
set by federal law, exceed an express requirement of state law (unless specifically
required by federal law), or exceed a requirement of a delegation agreement.
The rulemaking was not developed solely under the general powers of the agency,
but was specifically developed to meet the NAAQS established under federal
law and authorized under Texas Clean Air Act (TCAA), §§382.011,
382.012, 382.017, 382.019, and 382.039.
The commission invites public comment on the draft regulatory impact analysis.
TAKINGS IMPACT ASSESSMENT
The commission prepared a takings impact assessment for these rules in
accordance with Texas Government Code, §2007.043. The following is a
summary of that assessment. The specific purpose of the rulemaking action
is to establish a lawn and garden service equipment operating-use limitation
to delay NO
x
emissions that lead to high levels
of ground-level ozone production. This proposed rulemaking 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. The proposed
affected area consists of the eight counties contained in the HGA CMSA. Promulgation
and enforcement of the proposed rules will not burden private, real property
as it only regulates handheld and non-handheld spark-ignition lawn and garden
equipment rated at 25 hp or less. Although the proposed 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 proposed rules
partially fulfill a federal mandate under 42 USC, §7410. Specifically,
the emissions limitations and delays within this proposal 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 the rule proposal is to implement
a lawn and garden service equipment operating-use limitation necessary for
the HGA nonattainment area to meet the air quality standards established under
federal law as NAAQS. Consequently, the exemption which also applies to these
proposed rules is that of an action reasonably taken to fulfill an obligation
mandated by federal law. For the reasons stated, these proposed rules will
not constitute a takings under the Texas Government Code, Chapter 2007.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that the proposed 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 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.
Interested persons may submit comments on the consistency of the proposed
rules with the CMP during the public comment period.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic
Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central
Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite
200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource
Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin.
The hearings are structured for the receipt of oral or written comments by
interested persons. Registration will begin one hour prior to each hearing.
Individuals may present oral statements when called upon in order of registration.
A four-minute time limit will be established at each hearing to assure that
enough time is allowed for every interested person to speak. Open discussion
will not occur during each hearing; however, agency staff members will be
available to discuss the proposal one hour before each hearing, and will answer
questions before and after each hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend a hearing, should contact the Office of
Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087,
faxed to (512) 239-4808, or emailed to
siprules@tnrcc.state.tx.us
. All comments should reference Rule Log Number 2000-011O-114-AI. Comments
must be received by 5:00 p.m., September 25, 2000. For further information,
please contact Roland Castaneda at (512) 239-0774, or Alan Henderson at (512)
239-1510.
STATUTORY AUTHORITY
The new sections are proposed under the 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 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 proposed 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.
The proposed new sections implement TCAA, §382.002, relating to Policy
and Purpose; §382.011, relating to General Powers and Duties; §382.012,
relating to State Air Control Plan; §382.019, relating to Methods Used
to Control and Reduce Emissions from Land Vehicles; and §382.039, relating
to Attainment Program.
§114.452.Control Requirements.
No person shall start or operate any handheld or non-handheld, spark-ignition
lawn and garden service equipment, of 25 horsepower and below, between the
hours of 6:00 a.m. and noon, during the time period between April 1 through
October 31, in the counties listed in §114.459 of this title (relating
to Affected Counties and Compliance Dates).
§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, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery,
and Waller Counties in the Houston/Galveston ozone nonattainment area.
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005627
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
30 TAC §§114.460, 114.462, 114.466, 114.469
The Texas Natural Resource Conservation Commission (commission)
proposes new §114.460, Definitions; §114.462, Control Requirements; §114.466,
Reporting and Recordkeeping Requirements; and §114.469, Affected Counties
and Compliance Schedules. The commission proposes these new sections in Chapter
114, Control of Air Pollution from Motor Vehicles; Subchapter I, Non-Road
Engines; new Division 7, Houston/Galveston Airport Ground Support Equipment;
and corresponding revisions to the state implementation plan (SIP) in order
to control ground-level ozone in the Houston/Galveston (HGA) ozone nonattainment
area through the reduction of nitrogen oxide (NO
x
)
emissions from airport ground support equipment (GSE).
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED 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. 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 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. 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 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,
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 included in
this proposal indicates a gap of an additional 77.98 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 5.09 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 have formally submitted a resolution to
the commission, requesting the inclusion of many specific emission reduction
strategies.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses 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
Airport GSE rules were adopted by the commission for the Dallas/Fort Worth
(DFW) nonattainment area on April 19, 2000. This rulemaking action proposes
identical requirements applied to the eight-county HGA ozone nonattainment
area and are necessary for the area to be able to demonstrate attainment with
the ozone NAAQS.
Airport GSE is used from the moment an aircraft lands, until the aircraft
takes off. Airport GSE is comprised of a variety of vehicles and equipment
necessary to service aircraft during ground-based operations, including cargo
loading and unloading, passenger loading and unloading, potable water storage,
lavatory waste tank drainage, aircraft refueling, engine and fuselage examination
and maintenance, and food and beverage catering. Airlines employ specially
designed GSE to support all these operations. Moreover, electrical power and
conditioned air are generally required during aircraft operations at the terminal
gate to provide comfort and safety for the passengers and crew. These services
are often provided by the terminal facility, however many times these services
are provided by GSE. Airport GSE includes, but is not limited to, aircraft
pushback tugs, baggage and cargo tugs, carts, forklifts, lifts, ground power
units, air conditioning units, air start units, and belt loaders. Electric-powered
versions of baggage tugs and belt loaders, which represent about a third of
all GSE, are available and in use. Electric-powered versions of aircraft pushback
tugs, air start units, air conditioning units, forklifts, lifts, ground power
units, and other specialty GSE are also available in the marketplace.
The initial purchase cost of electric-powered GSE is typically higher than
diesel-powered and gasoline-powered GSE. A recent report by the EPA,
The majority of GSE engines are "uncontrolled" from an emission perspective,
because they have not been designed for low emissions. Therefore, GSE emits
significant amounts of VOC and NO
x
. The EPA report
(420-R-99-007) states that GSE is responsible for 15%-20% of airport-related
NO
x
and 10%-15% of airport-related VOC. The replacement
of internal combustion engine-powered GSE with low-or zero-emission GSE at
the airports where this equipment is used will reduce the VOC and NO
The commission solicits 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.
SECTION-BY-SECTION DISCUSSION
Rules regarding airport GSE were adopted for the DFW ozone nonattainment
area on April 19, 2000. These rules were adopted in Chapter 114, Subchapter
I, Division 1, §114.400, Definitions; §114.402, Control Requirements; §114.406,
Reporting and Recordkeeping Requirements; and §114.409, Affected Counties.
This rulemaking action proposes identical requirements in Subchapter I, Division
7 which would apply to the eight-county HGA ozone nonattainment area.
The proposed new §114.460 includes definitions for air carrier, air
carrier operations, ground support equipment, ground support equipment fleet,
GSE average emission factor, and subject airport.
The proposed new §114.462(a), explains that affected owners and operators
of GSE must demonstrate a NO
x
emissions reduction
which is equal to or greater than the percentages of NO
x
emissions attributable to the GSE fleet during the 1996 calender
year. These reductions must be made in accordance with the following schedule:
20% reduction by December 31, 2003; 50% reduction by December 31 2004; and
90% reduction by December 31, 2005. Subsection (b) pertains to those fleets
which were not in operation in 1996. Using the emission factors from §114.460(6),
the owner and/or operator of the fleet must demonstrate the following NO
The proposed new §114.462(d) allows the commission to better enforce
the rule by providing that each entity that chooses not to fully electrify
its fleet shall submit a plan to the commission by May 1, 2003, or the first
May 1st following operation at a subject airport. This plan shall list each
GSE unit, its horsepower rating, its emission factor, the total actual annual
emissions for each unit in existence in 1996, and provide for the implementation
of emission reduction measures to achieve NO
x
emissions in the amount required by §114.462(a), (b), (c), and (e). To
provide alternate means of compliance while still achieving emission reductions,
the plan may include emission reductions measures which are applied to the
GSE fleet itself, and measures which have been achieved elsewhere in the nonattainment
area if those measures would be creditable under the commission emissions
banking program as defined in 30 TAC §101.29. This plan must be approved
by the executive director and the EPA, and should be revised as needed to
accurately reflect the compliance plan. New subsection (e) ensures emission
reductions for growth after 1996, specifying that beginning December 31, 2004,
owners and operators of GSE subject to §114.462(a), (b), or (c) must
demonstrate that their non-electric GSE units added to the fleet after December
31, 1996, or after the first year of being subject to the rule, are offset
by 90%. Subsection (f) states that the requirements of any enforceable agreement
between the EPA, the United States Department of Transportation, and the GSE
owners/operators may be included in a plan submitted under §114.462(d).
The proposed new §114.462(g) states that in lieu of compliance with §114.462(a)-(e)
an owner or operator of GSE at a subject airport may ensure that the fleet
is 100% electric powered by May 1, 2005, or three years after the airport
becomes a subject airport. Additionally, §114.462(g) states that for
any GSE unit not available for purchase or conversion to electric power, an
owner or operator of GSE may meet the requirements of this subsection if it
can be shown that the lowest emitting equipment is being used, subject to
approval by the executive director and the EPA.
The proposed new §114.466(a) requires that owners or operators subject
to §114.462 submit annual GSE fleet reports to be submitted to the executive
director. Subsection (b) requires them to maintain copies of the submitted
reports for a minimum of three years. For convenience, the commission will
permit these reports to be kept in hard-copy or electronic form.
The proposed new §114.469 identifies the counties subject to these
rules as being Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty,
Montgomery, and Waller Counties. These counties make up the HGA ozone nonattainment
area.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT
John Davis, Technical Specialist with Strategic Planning and Appropriations,
determined that for the first five-year period these proposed rules are in
effect there will be no significant fiscal implications for units of state
and local government as a result of administration or enforcement of the rules.
The airlines and businesses that serve the George Bush Intercontinental, William
P. Hobby, and Ellington Airports in Harris County will probably incur relatively
high costs for the first five-year period of the proposed rules due to the
purchase/lease of cleaner operating GSE needed to meet reduced emission requirements
at subject airports; however, those initial costs will be offset by reduced
maintenance and fuel costs over time (especially in the case of electric-powered
GSE).
The proposed rules will require airports in the eight-county HGA nonattainment
area to comply with requirements identical to the existing GSE emission reduction
requirements operated at airports in the DFW area. Affected airports are those
with 100 or greater air carrier operations per year (excluding general aviation
operations, non-fixed wing operations, and military operations), averaged
over a three-year period. Owners or operators of GSE subject to this section
at the time of the effective date must demonstrate the following emission
reductions based on 1996 NO
x
emissions levels:
20% reduction by December 31, 2003; 50% reduction by December 31, 2004; and
90% reduction by December 31, 2005. Owners or operators of GSE not in operation
in 1996 at an airport which is a subject airport by the effective date of
this rule must demonstrate a reduction of NO
x
emissions which is equal to or greater than the following percentages: 20%
reduction by December 31, 2003, or December 31 of the first year of operation,
whichever is later; 50% reduction by December 31, 2004, or December 31 of
the second year of operation, whichever is later; and 90% reduction by December
31, 2005, or December 31 of the third year of operation, whichever is later.
Owners and operators of affected GSE will also be required to submit annual
GSE fleet reports to the commission. The reporting is designed to demonstrate
compliance with the implementation schedule. This air pollution control program
is part of the 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 City of Houston, which owns and operates the three affected airports,
will be affected if they own or operate GSE. Additionally, there may be costs
to the city related to the possible addition or retrofitting of infrastructure
which accommodate alternative-fueled GSE at the affected airports. Infrastructure
costs for full electrification of GSE at the four affected airports in the
DFW area have been estimated by the Air Transport Association to be approximately
$70 million. Presumably estimates for Houston could be similar. Actual infrastructure
costs are expected to be lower depending upon the compliance options chosen.
The City of Houston could pass some or all of these costs on to its tenants
at the airports. The local air pollution control agency having jurisdiction
in the area may request reports relating to §114.406 as well. There are
no significant fiscal implications anticipated for the City of Houston or
other units of state and local government as a result of administration of
the proposed rules, except as mentioned in the previous paragraphs.
PUBLIC BENEFIT AND COSTS
Mr. Davis also determined that for each year of the first five years the
proposed rules are in effect, the public benefit anticipated from enforcement
of and compliance with the proposed rules will be the potential reduction
in NO
x
emissions from affected airports, potentially
improved air quality, and contribution toward demonstration of attainment
with the ozone NAAQS within the HGA nonattainment area.
Although GSE owners and operators have a number of options to reduce NO
At George Bush Intercontinental Airport, the following airlines will be
affected: AeroMexico, American, America West, British Airways, Canadian Airlines,
Continental, Delta, Northwest, TWA, United, US Airways, Atlantic Southeast,
Lufthansa, Sun Country, KLM Royal Dutch, Comair, Air France, Air Canada, TACA,
Federal Express, BAX Global, Aeromexpress, American International, and Trans
World Airlines. At William P. Hobby Airport, AirTran, American, Atlantic Southeast,
Continental, Delta, Northwest, and Comair will be affected. At Ellington Airport,
United Postal Service will be affected. Other businesses at the three affected
airports that support airline operations and use GSE will also be required
to adhere to the GSE NO
x
emission reduction requirements
found in these rules. Tenant entities at the affected airports could be affected
by infrastructure costs detailed in the Fiscal Note: Cost to State and Local
Government section of this preamble.
The EPA report (420-R-99-007), indicates the cost savings for electric-powered
GSE, initial purchase costs for electric GSE are high relative to their fossil-fueled
counterparts. The cost premium is almost entirely associated with the required
battery pack and recharger. Table I, Life Cycle Costs for Baggage Tractors,
presents a comparison of electric baggage tractor initial costs relative to
those of fossil-fueled GSE. As indicated, the cost premium ranges from about
$8,000 relative to a diesel-powered tractor, to about $13,000 relative to
a gasoline-powered tractor. These purchase price premiums are augmented by
periodic battery replacement requirements (at about $4,500 every five to six
years) that are two to four times higher on a life cycle basis than corresponding
fossil fuel engine rebuild or replacement costs. However, these cost premiums
are counterbalanced by a substantial reduction in fuel costs. Electric GSE
use no fuel during idle periods and such periods can comprise as much as 50%
of typical GSE operation. Using an estimated electricity cost of $.045 per
kilowatt-hour, the overall fuel savings associated with high-use GSE operations,
such as baggage tractors, can range from $2,500 per year relative to diesel
equipment to over $6,000 per year relative to gasoline and compressed natural
gas equipment. While lower-use GSE fuel cost savings will be smaller, it is
clear that fuel savings alone can offset the entire electric GSE purchase
price premium in two to three years. Moreover, electric GSE fuel cost savings
will increase as more efficient electric motors and motor controllers continue
to evolve.
In addition to reduced fuel costs, the latest generation of electric GSE
have demonstrated significantly reduced maintenance requirements. Costs have
been estimated to be reduced by as much as two-thirds relative to gasoline-and
diesel-powered GSE. The table presents the results of a life cycle cost comparison
for a baggage tractor under a high-use operating scenario (i.e., generally
used to service aircraft continuously throughout an operating day such as
occurs at high traffic airports). The tabulated costs represent the net present
value of the various expenditures required over the 16-year useful life of
the tractor. Regardless of whether maintenance costs are assumed to be reduced,
the electric-powered tractor consistently exhibits the lowest life cycle costs.
Life cycle costs for the electric baggage tractor are estimated to be over
40% lower than the next lowest cost diesel option under a reduced maintenance
scenario, and still 10% lower even if maintenance costs are assumed to be
identical to conventional gasoline-and diesel-powered GSE maintenance costs.
Precise cost effectiveness estimates for electric GSE are difficult to
quantify because the impact of such equipment varies across the pollutants
examined and relative to the fossil fuel equipment being replaced, and the
emissions performance of local utilities. However, it is clear from the data
presented in the table that electric GSE represent the lowest cost option
relative to all fossil fuel GSE. Therefore, if an appropriate battery recharging
schedule and infrastructure can be established, all derived emission reductions
accrue for free. Assuming local utility emissions performance is not too different
from average United States utility emission levels, electric GSE are cost
effective from an economic standpoint alone.
Figure: 30 TAC Chapter 114E-Preamble
The EPA report also stated that " . . . generally, there are no technical
limitations to the size or type of GSE that can be converted to or replaced
with electrically powered equipment. Electrically powered versions of baggage
tugs and belt loaders, which together account for over a third of all GSE,
are available and in use (although current usage constitutes only a minor
fraction of total activity). Additionally, electric powered versions of aircraft
pushback tractors, air start units, conditioned air units, forklifts, ground
power units, lifts, general purpose vehicles (cars, trucks, and vans), and
other specialty GSE are currently available in the marketplace. Electric carts
are already fulfilling about half of overall GSE cart demand."
The following is an excerpt from a study titled
Assessment of Airport Ground Support Equipment Using Electric Power or Low-Emitting
Fuels
(Arcadis, Geraghty and Miller, July 20, 1999) that indicates
the costs for electric-powered GSE. The study estimated the purchase cost
for an electric baggage tractor to be $24,250; an electric belt loader to
be $30,000; and an electric aircraft tug to be $85,000. Their gasoline-powered
equivalents are $16,000, $27,000, and $72,000, respectively. The diesel-powered
equivalents are $19,000, $29,000, and $72,000, respectively. The study also
estimated the GSE population in California. If airport GSE population within
the HGA area is similar, then the baggage tractors make up 44%; belt loaders
make up 20%; and aircraft tugs make up 6% of the total GSE. If the estimated
3,154 pieces of GSE at the affected airports are equally proportioned and
assuming none of the current GSE is electric-powered, the commission estimates
that there are 1,388 baggage tractors, 631 belt loaders, and 189 aircraft
tugs. Applying the cost from the Geraghty and Miller study, the estimated
total cost for 70% of the equipment at the affected airports is $68.6 million.
Assuming that the remaining 30% of the equipment, or 946 units, are lower
cost equipment in the $10,000 to $20,000 range, the total cost should not
be in excess of $87.5 million less trade-in, transfer, or sale of current
equipment. As stated previously, the commission also anticipates that additional
costs associated with replacing current GSE with electric-powered GSE will
be offset with fuel and maintenance savings over time. The commission estimates
that the cost of the reporting requirements in the proposed rules will not
be significant.
SMALL BUSINESS AND MICRO-BUSINESS IMPACT ANALYSES
The commission anticipates no adverse fiscal implications to small businesses
and micro-businesses as a result of implementing the proposed rules, because
there are no known small or micro-businesses that own and operate GSE at the
George Bush Intercontinental, William P. Hobby, or Ellington Airports. If
there are small or micro-businesses that own GSE for the purpose of delivering
their products to the aircraft; providing maintenance support for aircraft
at affected airports; or renting/leasing GSE to airlines or related companies
which provide services to the airlines; their costs will be similar to those
specified for businesses in general in the PUBLIC BENEFITS AND COSTS section
of this preamble.
The Geraghty and Miller study estimated the costs for electric-powered
GSE. The study estimated the purchase cost for an electric baggage tractor
to be $24,250; an electric belt loader to be $30,000; and an electric aircraft
tug to be $85,000. The commission anticipates that some of the equipment used
by affected small or micro-businesses may be lower cost units in the $10,000
to $30,000 range. Actual total costs would be dependent on the amount and
types of GSE used by the business. The commission also anticipates that costs
will be mitigated by the trade-in, transfer, or sale of current equipment.
As stated previously, the commission anticipates that additional costs associated
with replacing current GSE with electric-powered GSE will be offset with fuel
and maintenance savings over time, and that the cost of the reporting requirements
in the proposed rules will not be significant.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the proposed 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 proposed rules 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.
The proposed rules regarding airports operating in the HGA ozone nonattainment
area, impose requirements to reduce the NO
x
emission
levels at the airports through the conversion of fossil-fueled GSE to electric-powered
GSE, or equivalent conversion measures which meet the required emission reduction
levels, over a three-to four-year period. This air pollution control program
is part of the strategy to reduce NO
x
emissions
necessary for the counties included in the HGA ozone nonattainment area to
be able to demonstrate attainment with the ozone NAAQS. Although the proposed
rulemaking meets the definition of a "major environmental rule" as defined
in the Texas Government Code, and is considered a major environmental rule, §2001.0225
only applies 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.
This rulemaking does not meet any of these four applicability requirements
of a "major environmental rule." Specifically, the proposed rules regarding
airports operating in the HGA ozone nonattainment area, impose requirements
to reduce the NO
x
emission levels at the airports
through the conversion of fossil-fueled GSE to electric-powered GSE, or equivalent
conversion measures which meet the required emission reduction levels. These
requirements are necessary to meet the ozone NAAQS set by the EPA under 42
USC, §7409, and therefore meet 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. 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 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. Thus, while specific measures are not generally required, the
emission reductions are required. 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.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code was amended by Senate Bill 633 (SB 633) during the
75th Legislative Session, 1999. The intent of SB 633 was to require agencies
to conduct a regulatory impact analysis (RIA) of extraordinary rules. These
are identified in the statutory language as 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. 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. For these reasons, rules proposed for
inclusion in the SIP fall under 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
reductions, such as those 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 obtain NO
x
emission reductions which 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 rulemaking does not exceed a standard
set by federal law, exceed an express requirement of state law (unless specifically
required by federal law), or exceed a requirement of a delegation agreement.
The rulemaking was not developed solely under the general powers of the agency,
but was specifically developed to meet the NAAQS established under federal
law and authorized under Texas Clean Air Act (TCAA), §§382.011,
382.012, 382.017, 382.019, and 382.039.
The commission invites public comment on the draft regulatory impact analysis
determination.
TAKINGS IMPACT ASSESSMENT
The commission prepared a takings impact assessment for this rulemaking
action in accordance with Texas Government Code, §2007.043. The following
is a summary of that assessment. The specific purpose of the rulemaking is
to require airport GSE to be electric-powered or to lower emissions by any
means available 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 to be able to demonstrate attainment
with the ozone NAAQS. The proposed affected area consists of the eight-county
HGA ozone nonattainment area, which includes Brazoria, Chambers, Fort Bend,
Galveston, Harris, Liberty, Montgomery, and Waller Counties. Promulgation
and enforcement of the rules may burden private real property, because this
proposed rulemaking action may result in investment in the permanent installation
of supplied utilities at the major airports in the HGA area. Although the
proposed 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 emission limitations and control requirements
within this proposal 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 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 proposal is to implement a GSE emissions reduction
program in the HGA ozone nonattainment area which is necessary for the area
to meet the air quality standards established under federal law as NAAQS.
Consequently, the exemption which applies to this rulemaking action is that
of an action reasonably taken to fulfill an obligation mandated by federal
law; therefore, these proposed rules will not constitute a takings under the
Texas Government Code, Chapter 2007.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that the proposed 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 Resource
Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter
281, Subchapter B, concerning 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 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.
Interested persons may submit comments on the consistency of the proposed
rules with the CMP during the public comment period.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El
Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments,
2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September
25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100
North I-35, Building E, Room 201S, Austin. The hearings are structured for
the receipt of oral or written comments by interested persons. Registration
will begin one hour prior to each hearing. Individuals may present oral statements
when called upon in order of registration. A four-minute time limit will be
established at each hearing to assure that enough time is allowed for every
interested person to speak. Open discussion will not occur during each hearing;
however, agency staff members will be available to discuss the proposal one
hour before each hearing, and will answer questions before and after each
hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend a hearing, should contact the Office of
Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087,
faxed to (512) 239-4808, or emailed to
siprules@tnrcc.state.tx.us
. All comments should reference Rule Log Number 2000-011E-114-AI. Comments
must be received by 5:00 p.m., September 25, 2000. For further information,
please contact Roland Castaneda at (512) 239-0774, or Alan Henderson at (512)
239-1510.
STATUTORY AUTHORITY
The new sections are proposed under the 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 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 proposed 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.
The proposed new sections implement TCAA, §382.002, relating to Policy
and Purpose; §382.011, relating to General Powers and Duties; §382.012,
relating to State Air Control Plan; §382.019, relating to Methods Used
to Control and Reduce Emissions from Land Vehicles; and §382.039, relating
to Attainment Program.
§114.460.Definitions.
Unless specifically defined in the TCAA or in the rules of the commission,
the terms used by the commission 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, the following words and terms, when used in this division,
shall have the following meanings, unless the context clearly indicates otherwise.
(1)
Air carrier--An entity providing air transportation of
persons or goods for remuneration.
(2)
Air carrier operation--Landings and takeoffs of air carriers
(excluding general aviation, non-fixed wing aircraft operations, and military
operations) at airports for the purpose of transportation of persons and/or
goods, or for the purpose of maintenance.
(3)
Ground support equipment (GSE)--Equipment that is used
to service aircraft during passenger and/or cargo loading and unloading, maintenance,
and other ground-based operations (excluding the servicing of general aviation
aircraft, non-fixed wing aircraft, and military aircraft). This includes,
but is not limited to, aircraft pushback tugs, baggage and cargo tugs, carts,
forklifts, lifts, ground power units, air conditioning units, air start units,
and belt loaders. Equipment that is used during freezing weather only is excluded
from this definition (including, but not limited to, ground heaters and deicing
vehicles).
(4)
Ground support equipment fleet--A group of ground support
equipment controlled by the owner or operator at the same location. For purposes
of compliance with the requirements of this division, a unit of GSE which
is leased on a long-term basis (12 months or more) shall be considered part
of the fleet of the lessee while a unit of GSE which is leased on a short-term
basis (less than 12 months) shall be considered part of the fleet of the lessor.
(5)
GSE average emission factor--For purposes of calculating
emission reductions needed for compliance with §114.462(b) of this title
(relating to Control Requirements), the following factor should be used depending
on engine size.
Figure: 30 TAC §114.460(5)
(6)
Subject airport--For purposes of compliance with this division,
airports which have more than or equal to 100 air carrier operations per year,
averaged over a three-year period. For airports which do not meet this average
operating level on the effective date of this rule, the date which the airport
becomes a subject airport is the January 1st following three years at or above
that average operating level.
§114.462.Control Requirements.
(a)
In the counties listed in §114.469 of this title (relating
to Affected Counties and Compliance Schedules), owners or operators of a ground
support equipment (GSE) fleet at an airport which was a subject airport by
the effective date of this rule must demonstrate a reduction of oxides of
nitrogen (NO
x
) emissions which is equal to or
greater than the following percentage of NO
x
emissions attributable to the GSE fleet during the 1996 calendar year in accordance
with the following schedule:
(1)
20% reduction by December 31, 2003;
(2)
50% reduction by December 31, 2004; and
(3)
90% reduction by December 31, 2005.
(b)
For a GSE fleet which was not in operation in 1996, owners
or operators of the GSE fleet at an airport which was a subject airport by
the effective date of this rule must demonstrate a reduction of NO
x
emissions which is equal to or greater than the following percentages
of the amount obtained by multiplying the number of non-electric GSE units
at the end of one year of operation by the GSE average emission factor as
defined in §114.460 of this title (relating to Definitions) in accordance
with the following schedule:
(1)
20% reduction by December 31, 2003 or December 31 of the
first year of operation, whichever is later;
(2)
50% reduction by December 31, 2004 or December 31 of the
second year of operation, whichever is later; and
(3)
90% reduction by December 31, 2005 or December 31 of the
third year of operation, whichever is later.
(c)
At an airport which becomes a subject airport after the
effective date of this rule, owners or operators of a GSE fleet shall meet
the emission reduction requirements of subsection (a) or (b) of this section
in accordance with the following schedule:
(1)
20% reduction by December 31, 2003 or December 31 of the
year the airport becomes a subject airport, whichever is later;
(2)
50% reduction by December 31, 2004 or December 31 of the
year after the airport becomes a subject airport, whichever is later; and
(3)
90% reduction by December 31, 2005 or December 31 of the
second year after the airport becomes a subject airport, whichever is later.
(d)
Each GSE fleet subject to this subsection shall submit
a plan to the executive director by May 1, 2003, or the first May 1st following
operation at a subject airport, which lists each GSE unit, an emission factor
for each unit, and the total actual annual emissions for each unit in existence
in calendar year 1996. The plan shall provide for the implementation of emission
reduction measures to achieve NO
x
emissions in
the amount required by subsections (a), (b), or (c) of this section. The plan
may include emission reductions measures which are applied to the GSE fleet
itself and measures which have been achieved elsewhere within the nonattainment
area as long as those measures would be creditable in accordance with the
commission's emissions banking program as defined in §101.29 of this
title (relating to Emission Credit Banking and Trading). The plan shall be
revised as necessary and is subject to the approval of the executive director
and the EPA.
(e)
Beginning in December 31, 2004, all owners or operators
of GSE fleets subject to subsections (a), (b), or (c) of this section must
demonstrate that emissions from any non-electric GSE added to the GSE fleet
after December 31, 1996, or after the first year of operation at a subject
airport, is offset by 90%. This subsection does not apply to GSE which is
added to the fleet to replace existing GSE.
(f)
In the event that the EPA, the United States Department
of Transportation, and the GSE owners/operators adopt an enforceable agreement,
the measures defined within that agreement may be used in a plan submitted
in accordance with subsection (d) of this section.
(g)
In lieu of compliance with subsections (a)-(e) of this
section, an owner or operator of a GSE fleet at a subject airport may ensure
that the fleet is 100% electric powered by May 1, 2005, or three years after
the airport became a subject airport, whichever is later. For any GSE unit
which is not available for purchase or conversion to electric power, an owner
or operator may meet the requirement of this subsection if the owner or operator
demonstrates that the lowest emitting equipment is used, subject to the approval
of the executive director and the EPA.
§114.466.Reporting and Recordkeeping Requirements.
(a)
Owners or operators affected by §114.462 of this title
(relating to Control Requirements) must submit annual ground support equipment
(GSE) fleet reports for the previous year starting on February 1, 2004, and
every February 1 thereafter. The report shall be submitted to the executive
director and must contain, at a minimum:
(1)
the GSE fleet identification number when assigned by the
commission;
(2)
area in which the affected GSE primarily operate;
(3)
the purchase date, make, model, model year, horsepower
rating, and fuel type for each unit of GSE;
(4)
a demonstration of compliance with the applicable control
requirements under §114.462 of this title; and
(5)
any other information requested in writing by the executive
director necessary to demonstrate compliance with this division.
(b)
The owner or operator of GSE shall maintain copies of submitted
reports required by subsection (a) of this section on-site either in hard
copy or electronically at the reported fleet address for a minimum of three
years, and upon request shall make such reports immediately available to the
executive director or local air pollution control agencies having jurisdiction
in the area.
§114.469.Affected Counties and Compliance Schedules.
Owners or operators of ground equipment at subject airports in Brazoria,
Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties
shall be in compliance with §114.462 of this title (relating to Control
Requirements) and §114.466 of this title (relating to Reporting and Recordkeeping
Requirements) no later than the dates specified therein.
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005647
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 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)
proposes new §114.470, Definitions; §114.472, Control Requirements; §114.476,
Reporting and Recordkeeping Requirements; §114.477, Exemptions; and §114.479,
Affected Counties. The commission proposes these revisions to 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 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.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED 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. 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 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 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
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,
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 included in
this proposal indicates a gap of an additional 77.98 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
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 have formally submitted a resolution to
the commission, requesting the inclusion of many specific emission reduction
strategies.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses 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 proposes 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 proposed rules are one element of the control strategy for the
HGA Post-1999 ROP/Attainment Demonstration SIP. The purpose of these proposed
rules is to establish the accelerated purchase and operation of 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, to be phased in over several years beginning
in model year 1999. 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 114C-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 proposed new rules would 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. In other words, non-road equipment
does 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 proposed rules will require persons in the HGA nonattainment area which
own or operate 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 proposed 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 proposed 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 proposed rules exempt non-road
engines used in locomotives, underground mining equipment, marine application,
aircraft, airport ground support equipment (GSE), equipment used solely for
agricultural purposes, emergency equipment, and freezing weather equipment.
Generally, the rules will affect equipment 50 hp and larger used in construction,
general industrial, lawn and garden, utility, and material handling applications.
Examples of equipment used in construction applications include backhoes,
bore/drill rigs, cement mixers, crawler tractors, excavators, graders, off-highway
trucks, pavers, paving equipment, plate compactors, rollers, rubber-tire dozers,
rubber-tire loaders, scrapers, signal boards, skid-steer loaders, trenchers,
and feller/bunchers. Examples of equipment used in general industrial applications
include concrete/industrial saws, crushing equipment, oil field equipment,
refrigeration/air conditioning units, scrubber/sweepers, and rail maintenance
equipment. Examples of equipment used in lawn and garden applications include
garden tractors, rear engine mowers, and chipper/grinders. Examples of equipment
used in utility applications include air compressors, hydro-power units, pressure
washers, pumps, generator sets, irrigation sets, and welders. Examples of
equipment used in material handling applications include aerial lifts, cranes,
forklifts, and rough-terrain forklifts.
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 solicits 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.
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 proposes identical requirements
which would apply to the eight-county HGA ozone nonattainment area.
The proposed 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 proposed new §114.472 would require 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 schedule 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 proposes 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 proposed 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 proposed 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 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 proposed rule
will allow that 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 proposed 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 proposed new §114.476 requires persons subject to §114.472
to submit annual fleet reports. The proposed rule also requires them to maintain
copies of the submitted reports for a minimum of three years.
The proposed 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 this proposed rule because they are not regulated
by the EPA non-road rule. Airport GSE is exempt from this rule because it
is being regulated by another strategy being proposed concurrently. Agricultural
equipment is exempt from the proposed rule because of its small contribution
(less than 1.0%) to non-road emissions, and it is operated primarily in rural
areas. Also, the commission proposes 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 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 construction
equipment operating restrictions exemption comments and other comments to
those rules concerning the difficulty in complying with these rules, the commission
proposes §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 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 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 proposed by the
plans are equivalent to the reductions achieved from implementing both these
rules.
The proposed 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.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT
John Davis, Technical Specialist with Strategic Planning and Appropriations,
determined that for the first five-year period the proposed new sections are
in effect, there will be significant fiscal implications for units of state
and local government located within the HGA ozone nonattainment area that
own or operate non-road diesel vehicles and engines of 50 hp and larger.
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.
Tier 2 and 3 standards are EPA standards whose goals are to reduce NO
The proposed rules will affect the owners and operators of diesel equipment
of 50 hp and larger used in the construction, general industrial, lawn and
garden, utility, and material handling categories in the HGA ozone nonattainment
area. Examples of equipment in the construction category include backhoes,
bore/drill rigs, cement mixers, crawler tractors, excavators, graders, off-highway
trucks, pavers, paving equipment, plate compactors, rollers, rubber-tire dozers,
rubber-tire loaders, scrapers, signal boards, skid-steer loaders, trenchers,
and feller/bunchers. Examples of equipment in the general industrial category
include concrete/industrial saws, crushing equipment, oil field equipment,
refrigeration/air conditioning units, scrubber/sweepers, and rail maintenance
equipment. Examples of equipment used in the lawn and garden category include
garden tractors, rear engine mowers, and chipper/grinders. Examples of equipment
in the utility category include air compressors, hydro-power units, pressure
washers, pumps, generator units, irrigation units, and welders. Examples of
equipment in the material handling category include aerial lifts, cranes,
forklifts, and rough-terrain forklifts.
The proposed new rules will also require affected individuals, state and
local units of government, and businesses in the HGA area to submit to the
commission, annual reports that demonstrate compliance with the proposed new
sections. The proposed rules exempt non-road engines used in locomotives,
underground mining equipment, marine applications, aircraft, airport ground
support equipment, equipment used solely for agricultural purposes, emergency
equipment, and freezing weather equipment.
The total number of existing diesel equipment covered by the proposed new
sections and owned by units of state and local government is unknown; therefore,
the total cost to units of state and local government cannot be quantified.
As a sample of the potential equipment involved, the Texas Department of Transportation
has 137 pieces of equipment affected by these rules. The total cost to units
of state and local government will be similar to the costs discussed in the
PUBLIC BENEFITS AND COSTS section of this preamble and will vary with the
number of units owned that will need to be retrofitted, re-engined, or replaced
to comply with the proposed new sections.
PUBLIC BENEFIT AND COSTS
Mr. Davis also determined that for each year of the first five years the
proposed new sections are in effect, the public benefit anticipated from enforcement
of and compliance with the proposed new sections will be the potential reduction
of NO
x
, VOC, CO, and PM emissions, potentially
improved air quality, and contribution toward demonstration of attainment
with the ozone NAAQS.
The commission anticipates significant fiscal implications anticipated
to affected individuals, state and local government agencies, and businesses
as a result of implementing the proposed new sections.
The EPA's NONROAD computer model estimated a population, in calendar year
2007, of approximately 44,525 pieces of compression-ignition, non-road equipment
in the eight-county HGA ozone nonattainment area affected by the proposed
new sections. Based on the 1999 population of 34,609 pieces of compression-ignition,
non-road equipment in the eight-county HGA ozone nonattainment area, this
is a growth factor of approximately 3.2% per year. The commission estimates
that by the end of calendar year 1997, the population of compression-ignition,
non-road equipment in the eight-county HGA ozone nonattainment area was approximately
32,496 units. Using the ten year life-cycle for medium to large engines in
the EPA final regulatory impact analysis, approximately 12,969 units with
these types of engines will be purchased as a result of aging or growth from
the beginning of year 1998 through year 2000. This equipment will have to
be either retrofitted or re-engined with compliant engines or replaced during
years 2001 through 2007 in order to comply with the proposed new sections.
The commission estimates that approximately 9,264 units will be either retrofitted,
re-engined, or replaced from year 2001 through year 2005, the period covered
by this fiscal note. The commission assumes that retrofit, re-engine, or replacement
will begin in the year 2001. In the years following calendar year 2000, the
commission expects the population of compression-ignition, non-road units
to grow by 8,809 units through the end of calendar year 2007 to a total of
44,525 units. In addition, the commission estimates that another 22,747 aging
units will be replaced due to the normal life-cycle of this equipment. The
total of new units purchased due to growth and normal replacement is 31,556
units through year 2007. The commission estimates that approximately 22,340
of these units will be purchased during years 2001 through 2005 due to growth
and normal replacement.
The EPA's regulatory impact analysis contains estimated purchase prices
for new non-road diesel equipment. Two of these price estimates include new
portable and motive equipment in the 250 to 450 hp range and are applicable
to the proposed rule. The EPA estimated costs of $24,000 to $40,000 is for
new portable equipment in the 250 hp to 450 hp range. The EPA report does
not specify the types of the portable equipment, but the types could include
equipment like pumps, oil field equipment, refrigeration, and air conditioning
units. These types of equipment may be classified for the most part as industrial
equipment. In the EPA NONROAD model, the closest equivalent hp range is 175
hp to 300 hp. In that range, approximately 78 units must be retrofitted, re-engined,
or replaced through calendar year 2005 to comply with the proposed standards.
The estimated total replacement cost for these 78 units is an average of approximately
$373,502 to $622,503 per year from 2001 through the end of calendar year 2005.
The second EPA estimated cost is $130,000 for new motive equipment in the
250 hp to 450 hp range. The EPA does not specify the types of the motive equipment;
however, the motive equipment types in the NONROAD model are probably classified
as tractors and other related construction equipment. In the EPA NONROAD model,
there are 4,321 pieces of construction (motive) equipment in the 175 hp to
300 hp range by the end of calendar year 2007. In that size engine, approximately
899 units will be retrofitted, re-engined, or replaced from calendar year
2001 through 2005. The estimated replacement cost for these 899 units is an
average of approximately $23 million per year from 2001 through the end of
calendar year 2005.
Since the EPA study addressed the larger engines, the commission assumes
that approximately 7,971 of the remaining 8,286 units existing at the end
of calendar year 2000 in the HGA ozone nonattainment area that must be retrofitted,
or replaced are smaller units of equipment with replacement costs in the range
of $15,000 to $30,000. If the 7,971 smaller units of diesel non-road equipment
in the HGA ozone nonattainment area have replacement costs in the range of
$15,000 to $30,000, the estimated replacement cost for these units is an average
of approximately $24 million to $48 million per year from 2001 through the
end of calendar year 2005. The commission also assumes that 316 of the remaining
population of equipment with diesel engines in the HGA ozone nonattainment
area that must be retrofitted or replaced are larger units of equipment in
the $130,000 to $150,000 range. If the remaining 316 units of very large diesel,
non-road equipment in the HGA ozone nonattainment area have replacement costs
in the range of $130,000 to $150,000, the estimated replacement cost for these
units is an average of approximately $8 million to $9 million per year from
2001 through the end of calendar year 2005.
The commission estimates the cost impact to replace the 9,264 units of
non-road diesel equipment due to growth and replacement to meet standards
in the HGA ozone nonattainment area at the end of calendar year 2005 to be
an average of approximately $56 million to $81 million per year through the
end of calendar year 2005. This cost impact is based on the assumption that
all 9,264 units which will require modification or replacement through the
end of calendar year 2005 will be replaced with new equipment. It is probable
that some of this equipment will be retrofitted to meet either Tier 2 or Tier
3 standards, or re-engined with Tier 2 or Tier 3 compliant engines at costs
much lower than the replacement cost indicated here. It is also probable that
many equipment operators will choose to obtain equivalent emission reductions
without making any changes to their equipment. In addition, the commission
anticipates the total cost impact to be mitigated by the trade-in or the sale
of existing equipment if new equipment is purchased. However, over 96% of
this cost is based on the assumption that all of the 9,264 units that must
be retrofitted, re-engined, or replaced by the end of the calendar year 2005
will be replaced with all new equipment. The commission estimates that used
equipment in good condition is sold for from 40% to 60% of its original cost.
If a 50% factor is applied to replacement costs to offset the reduced cost
for retrofit, re-engine, and trade-in, the final cost impact to replace or
retrofit the 9,264 units is approximately $140 million to $203 million. The
decision to either purchase new equipment, retrofit, or re-engine will likely
be based on the economics for each unit of equipment.
Between the years 2001 and 2007, the EPA NONROAD computer model estimates
the population of diesel non-road equipment in the HGA ozone nonattainment
area to grow by 8,809 units. In addition, another 22,747 units will be purchased
to replace aging units for a total of 31,556 units. Approximately 22,340 of
the total 31,556 units purchased for growth and aging replacement will be
purchased during the years 2001 through 2005. The EPA analysis contains estimates
of domestic sales of various sizes of equipment. If the sales within the HGA
ozone nonattainment area are similar, the commission estimates that the additional
cost of the engines for this equipment would be an average of approximately
$2.1 million per year through the end of calendar year 2005. The EPA document
states that the costs of meeting the new 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%.
The commission estimates the total fiscal impact to replace the estimated
31,604 units of equipment which will be either purchased new, retrofitted,
re-engined, or replaced through 2005 to be an average of approximately $58
million to $83 million per year through calendar year 2005. Over 96% of this
cost is based on the assumption that all of the 31,604 units that must be
retrofitted, re-engined, or replaced by the end of calendar year 2005 will
be replaced with all new equipment. It is probable that some of this equipment
will be retrofitted to meet either Tier 2 or Tier 3 standards or re-engined
with Tier 2 or Tier 3 compliant engines at a much lower cost than replacement
cost. It is also probable that many equipment operators will choose to obtain
equivalent emission reductions without making any changes to their equipment.
In addition, the commission anticipates the total cost impact to be mitigated
by the trade-in or the sale of existing equipment if new equipment is purchased.
If trade-in allowances are considered, the commission anticipates the total
annual cost between the years 2001 to 2005 to be approximately $30 million
to $42 million. The decision to either purchase new equipment, retrofit, or
re-engine will likely be based on the economics for each unit of equipment.
The following table summarizes the costs through year 2005:
Figure 2: 30 TAC Chapter 114C-Preamble
SMALL BUSINESS AND MICRO-BUSINESS ASSESSMENT
The commission anticipates significant fiscal implications to small businesses
and micro-businesses located in the HGA ozone nonattainment area as a result
of implementing the proposed new sections. The commission anticipates that
there are many small and micro-businesses in the affected area that own and
operate non-road diesel equipment affected by the proposed rule. Depending
on the relative age of current equipment and the economics to retrofit or
re-engine the equipment versus new purchase for such equipment, affected small
and micro-businesses in the HGA ozone nonattainment area may have to retrofit,
re-engine, or replace some or most of their current diesel equipment in the
years 2001 through the end of calendar year 2007 in order to comply with the
proposed new sections. The commission anticipates that costs will be similar
to those for businesses at large as indicated in the PUBLIC BENEFIT AND COSTS
section of this preamble. The EPA estimated the costs of new portable equipment
in the 250 hp to 450 hp category at $24,000 to $40,000 and motive equipment
in the 250 hp to 450 hp range at approximately $130,000. The commission anticipates
that most effected small businesses or micro-businesses will own and operate
engines in the lower hp ranges, portable equipment, and other types of equipment
in the lower cost ranges of approximately $15,000 to $30,000 per unit. The
EPA estimated that the additional cost for diesel engines which comply with
the proposed standards are in the range of $240 to $1,900 each. The total
cost impact will be more dependent on the relative size of the fleet and on
the size and number of the non-road diesel equipment they own and operate.
The commission also anticipates that the total fiscal impact may be mitigated
by the trade-in or sale of existing equipment. The total number of existing
diesel equipment covered by the proposed new rules and owned by small and
micro-businesses is unknown; therefore, the total cost to small and micro-businesses
is undetermined.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the proposed rulemaking in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225, and determined
that the rulemaking is subject to §2001.0225 because it 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. The proposed new 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 proposed new 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
x
emissions necessary for the counties included
in the HGA ozone nonattainment area to be able to demonstrate attainment with
the ozone NAAQS. The commission proposes an air pollution control program,
including the use of Tier 2 and Tier 3 non-road, compression-ignition engine
standards, be established 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. Although the proposed rules
meet the definition of a "major environmental rule" 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 action does not meet any of these four applicability
requirements of a "major environmental rule." Specifically, the use of Tier
2 and Tier 3 non-road, compression-ignition engine standards within this proposal
were developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409,
and therefore meet 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. 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
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.
Thus, while specific measures are not generally required, the emission reductions
are required. 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.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code was amended by Senate Bill 633 (SB 633) during the
75th Legislative Session, 1999. The intent of SB 633 was to require agencies
to conduct a regulatory impact analysis (RIA) of extraordinary rules. These
are identified in the statutory language as 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. 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. For these reasons, rules proposed for
inclusion in the SIP fall under 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
reductions, such as those 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 obtain NO
x
emission reductions which 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 rulemaking does not exceed a standard
set by federal law, exceed an express requirement of state law (unless specifically
required by federal law), or exceed a requirement of a delegation agreement.
The rulemaking was not developed solely under the general powers of the agency,
but was specifically developed to meet the NAAQS established under federal
law and authorized under Texas Clean Air Act (TCAA), §§382.011,
382.012, 382.017, 382.019, and 382.039.
The commission invites public comment on the draft regulatory impact analysis.
TAKINGS IMPACT ASSESSMENT
The commission prepared a takings impact assessment for this rulemaking
action in accordance with Texas Government Code, §2007.043. The following
is a summary of that assessment. The specific purpose of the proposed 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 proposed 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. Although
the proposed rule does not directly prevent a nuisance, or prevent an immediate
threat to life or property, it does 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
the proposed rule 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 this rule is to implement a cleaner-burning, non-road, compression-ignition
fleet program necessary for the HGA nonattainment area to meet the air quality
standards established under federal law as NAAQS. Consequently, the exemption
which applies to this rulemaking action is that of an action reasonably taken
to fulfill an obligation mandated by federal law. Therefore, these proposed
rules will not constitute a takings under Texas Government Code, Chapter 2007.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that the proposed 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.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic
Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central
Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite
200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource
Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin.
The hearings are structured for the receipt of oral or written comments by
interested persons. Registration will begin one hour prior to each hearing.
Individuals may present oral statements when called upon in order of registration.
A four-minute time limit will be established at each hearing to assure that
enough time is allowed for every interested person to speak. Open discussion
will not occur during each hearing; however, agency staff members will be
available to discuss the proposal one hour before each hearing, and will answer
questions before and after each hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend a hearing, should contact the Office of
Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087;
faxed to (512) 239-4808; or emailed to
siprules@tnrcc.state.tx.us
. All comments should reference Rule Log Number 2000-011C-114-AI. Comments
must be received by 5:00 p.m., September 25, 2000. For further information,
please contact Ken Gathright at (512) 239-0599 or Alan Henderson at (512)
239-1510.
STATUTORY AUTHORITY
The new sections are proposed 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 authorizes the commission to adopt rules consistent with the policy
and purposes of the TCAA. The new sections are also proposed 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.
The proposed new sections implement TCAA, §382.002, relating to Policy
and Purpose; §382.011, relating to General Powers and Duties; §382.012,
relating to State Air Control Plan; §382.019, relating to Methods Used
to Control and Reduce Emissions from Land Vehicles; and §382.039, relating
to Attainment Program.
§114.470.Definitions.
Unless specifically defined in the TCAA or in the rules of the commission,
the terms used by the commission 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, the following words and terms, when used in this division,
shall have the following meanings, unless the context clearly indicates otherwise.
(1)
Blue Sky Series engine--A non-road engine meeting the requirements
of Title 40 Code of Federal Regulations (CFR) §89.112(f), as amended
on October 23, 1998.
(2)
Compression-ignition engine--A type of engine with operating
characteristics significantly similar to the theoretical diesel combustion
cycle. The non-use of a throttle to regulate intake air flow for controlling
power during normal operation is indicative of a compression-ignition engine.
(3)
Fleet--The aggregate of non-road equipment powered by compression-ignition
engines that operate within the counties specified in §114.479 of this
title (relating to Affected Counties) under the authority of the same person.
Regarding fleet equipment leased for one year or longer, the authority is
considered to reside with the lessee. For fleet equipment leased for less
than one year, the authority is considered to reside with the lessor.
(4)
Non-road engine--An engine as defined in Title 40 CFR §89.2,
as amended on December 29, 1999.
(5)
Non-road equipment--Equipment which is powered by a non-road
engine and which is not licensed for on-road use.
(6)
Tier 2 engine--An engine subject to the Tier 2 emission
standards listed in Title 40 CFR §89.112(a), Table 1, as amended on October
23, 1998.
(7)
Tier 3 engine--An engine subject to the Tier 3 emission
standards listed in Title 40 CFR §89.112(a), Table 1, as amended on October
23, 1998.
§114.472.Control Requirements.
(a)
Persons who own or operate non-road equipment powered by
compression-ignition engines 50 horsepower (hp) and larger, in the counties
listed in §114.479 of this title (relating to Affected Counties), are
subject to the compliance requirements specified in subsection (b) of this
section.
(b)
Owners or operators shall ensure that their fleet is certified
to meet or exceed the Tier 2 and Tier 3 standards in accordance with the following
schedule.
(1)
For the part of the fleet greater than or equal to 50 and
less than 100 hp:
(A)
at least 25% of the affected portion of the fleet shall
meet Tier 2 certification standards by December 31, 2004;
(B)
at least 50% of the affected portion of the fleet shall
meet Tier 2 certification standards by December 31, 2005;
(C)
at least 75% of the affected portion of the fleet shall
meet Tier 2 certification standards by December 31, 2006; and
(D)
100% of the affected portion of the fleet shall meet Tier
2 certification standards by December 31, 2007.
(2)
For the part of the fleet greater than or equal to 100
and less than or equal to 750 hp:
(A)
at least 10% of the affected portion of the fleet shall
meet Tier 2 certification standards by December 31, 2004;
(B)
at least 20% of the affected portion of the fleet shall
meet Tier 2 certification standards by December 31, 2005;
(C)
at least 30% of the affected portion of the fleet shall
meet Tier 2 certification standards by December 31, 2006; and
(D)
at least 50% of the affected portion of the fleet shall
meet Tier 3 certification standards, and the remainder of the affected portion
of the fleet shall meet Tier 2 certification standards by December 31, 2007.
(3)
For that part of the fleet with an hp rating greater than
750 hp:
(A)
at least 50% of the affected portion of the fleet must
meet Tier 2 certification standards by December 31, 2006; and
(B)
100% of the affected portion of the fleet must meet Tier
2 certification standards by December 31, 2007.
(c)
Non-road equipment that uses a "Blue Sky Series" engine,
as defined in §114.470 of this title (relating to Definitions) may be
considered a Tier 2 or Tier 3 engine for compliance with the percentage requirements
of subsection (b) of this section.
(d)
The percentage requirements of subsection (b) of this section
may also be met by a retrofit of currently owned or newly purchased non-road,
compression-ignition engines certified by the EPA to meet or exceed the Tier
2 or Tier 3 emission standards.
§114.476.Reporting and Recordkeeping Requirements.
(a)
Persons affected by §114.472 of this title (relating
to Control Requirements) must submit annual reports for the previous year
beginning February 1, 2005, and every February 1 thereafter. The report shall
be submitted to the executive director and shall contain, at a minimum:
(1)
the fleet identification number (when assigned by the Texas
Natural Resource Conservation Commission);
(2)
the person's name, mailing address, telephone and fax numbers;
(3)
the name, title, mailing address, and telephone number
of the specified person responsible for the fleet;
(4)
a list of all non-road equipment with compression-ignition
engines 50 horsepower and larger; and
(5)
a demonstration of compliance with the applicable implementation
schedule under §114.472 of this title.
(b)
The affected person shall maintain copies of reports required
by subsection (a) of this section on-site at the reported fleet address for
a minimum of three years, and upon request shall make such reports available
to the executive director or local air pollution control agencies with jurisdiction.
§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 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, that is approved by the executive director and the EPA by
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. In order to be approved, the plan must demonstrate reductions of oxides
of nitrogen emissions equivalent to those required by §114.472 of this
title and must contain adequate enforcement provisions.
§114.479.Affected Counties.
Persons in the following counties shall be in compliance with §114.472
and §114.476 of this title (relating to Control Requirements; and Reporting
and Recordkeeping Requirements) no later than the dates specified in §114.472(b)
of this title: Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty,
Montgomery, and Waller.
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005613
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 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)
proposes new §114.482, Control Requirements; §114.486, Recordkeeping
Requirements; §114.487, Exemptions; and §114.489, Affected Counties
and Compliance Dates. The commission proposes 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
proposes 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 proposed sections are one element of the control strategy for the
proposed HGA Post-1999 Rate-of-Progress (ROP)/Attainment Demonstration SIP.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED 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. 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. 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: The 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
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 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 included in
this proposal indicates a gap of an additional 77.98 tons per day (tpd) of
NO
x
reductions is necessary for an approvable
attainment demonstration.
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.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses 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
construction 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 later in the day, thus limiting 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 proposed revisions provide a similar restriction on the use of construction
equipment previously adopted by the commission for the Dallas/Fort Worth (DFW)
ozone nonattainment area, except for the effective period, which is between
the hours of 6:00 a.m. and noon, during Daylight Savings Time, which begins
on the first Sunday in April and ends on the last Sunday in October, for the
HGA ozone nonattainment area. The affected area includes the eight-county
HGA nonattainment area of Brazoria, Chambers, Fort Bend, Galveston, Harris,
Liberty, Montgomery, and Waller Counties. The contribution towards the reduction
in ozone levels from restricting the hours of operation of construction equipment
is an essential component of the control strategy and is necessary for the
eight-county HGA ozone nonattainment area to demonstrate attainment with the
ozone NAAQS.
The effective date of the amended rules for HGA will be April 3, 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 equipment become effective.
The equipment to which the rules concerning restrictions on the operation
of construction equipment apply includes all non-road, heavy-duty diesel equipment
classified as "construction equipment," rated at 50 hp and greater, regardless
of how it 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 operations are covered by these rules concerning restrictions
on the operation of construction equipment. It is not the commission's intent
to restrict the use of agriculture equipment, which does not meet the definition
of construction equipment.
The commission understands that a literal interpretation of the term "construction
equipment" could lead the reader to believe that the rules concerning restrictions
on the operation of construction equipment only applied to non-road, heavy-duty
diesel equipment used only for purposes of construction and mining, when in
fact, the rules apply to all construction equipment greater than 50 hp, regardless
of how it is being used.
Construction equipment is considered to be, but is not limited to, pavers,
paving equipment, plate compactors, rollers, scrapers, 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.
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 VOC 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 Daylight Savings Time in the HGA nonattainment area, the 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 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 anticipated and discussed by the EPA in their off-road
mobile source rules.
As established in the previously adopted DFW rules concerning restrictions
on the operation of construction equipment, the proposed rules contain exemptions
from control and recordkeeping requirements. These exemptions include construction
equipment used exclusively for emergency operations to protect public health
and the environment, and for mixing, transporting, pouring, or processing
wet concrete. Also, the proposed rules contain an exemption that allows operators
that submit an emissions reduction plan (plan) by May 31, 2002, which is approved
by the executive director and the EPA by May 31, 2003, to operate during the
restricted hours. The commission anticipates that by offering this exemption,
equipment manufacturers or regulated businesses will invest in research and
development of emissions-reducing technology for construction equipment to
enable affected businesses to meet the exemption.
The emission reduction plan must describe in detail how the operator will
modify his behavior or fleet of equipment to reduce NO
x
emissions by the implementation date in 2005 by a target amount equivalent
to the total NO
x
reductions achieved by implementation
of the rule from which the operator is applying for exemption. Owners or operators
may submit plans to apply for exemption from either the construction equipment
operating restriction rule or the accelerated purchase of non-road heavy-duty
diesel equipment rule, or from both rules. The plans must contain emission
reductions equivalent to the total NO
x
reductions
achieved by the rule from which they are applying for exemption and must contain
adequate enforcement provisions. Examples of modifications that 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).
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).
The commission will apply emission inventory factors for construction equipment
used in the modeling utilized in the development of the rules concerning restrictions
on the operation of construction equipment to quantify the NO
x
and VOC emission reductions and equivalent ozone 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 concerning restrictions
on the operation of construction equipment, and will offer guidance on how
to calculate total emissions reductions for a fleet of equipment. The commission
estimates that this measure results in an approximate 8.0 tpd shift of NO
The commission is requiring submission of the plans by May 31, 2002 to
allow sufficient time to review and quantify the collective emissions 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
achieved from implementing the underlying exempted rule. The commission will
implement the construction equipment operating restrictions rules on April
3, 2005 and the accelerated purchase rules on December 31, 2004, as proposed,
for operators who did not submit plans or whose plans were not approved.
Because this proposed strategy does not create an actual reduction in emissions
nor require the use of additional control equipment or any new technology,
the commission estimated 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 coincide with the hours
of operation allowed under the regulation.
The commission solicits 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.
SECTION BY SECTION DISCUSSION
The new Division 9 is proposed regarding HGA construction equipment operating
restrictions in order to provide an opportunity for comment on the complete
control strategy.
The proposed new §114.482 establishes control requirements for construction
equipment operating restrictions. The proposal restricts the operation of
any non-road diesel construction equipment of 50 hp and above, between the
hours of 6:00 a.m. and noon, during Daylight Savings Time, which begins on
the first Sunday in April and ends on the last Sunday in October.
The proposed new §114.486 requires all persons subject to the provisions
of §114.482 to maintain daily records of equipment operation in the affected
counties.
The proposed new §114.487 establishes exemptions from the control
requirements of §114.482 and the recordkeeping requirements of §114.486.
These exemptions include diesel equipment used exclusively for situations
involving emergency operations and diesel equipment while being used for mixing,
transporting, pouring, or processing of wet concrete. The commission understands
the definition of emergency equipment includes equipment which may have to
be used to repair facilities or devices which have failed in order to prevent
greater immediate environmental harm. Also, the proposed rules contain an
exemption that allows operators that submit an emissions reduction plan by
May 31, 2002, which is approved by the executive director and the EPA by May
31, 2003, to operate during the restricted hours.
The proposed new §114.489 specifies the counties which are subject
to the new requirements and the dates and times these counties are subject
to these requirements. The affected counties include all eight counties in
the HGA ozone nonattainment area, which include Brazoria, Chambers, Fort Bend,
Galveston, Harris, Liberty, Montgomery, and Waller Counties. The compliance
date for the HGA area is April 3, 2005.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT
John Davis, Technical Specialist with Strategic Planning and Appropriations,
has determined that for the first five-year period that the proposed rules
are in effect, significant fiscal implications are anticipated for units of
state and local government as a result of administration or enforcement of
the proposed rules. The proposed rules would restrict the use of heavy-duty
diesel construction equipment, rated at 50 hp and greater, from use between
the hours of 6:00 a.m. and noon, during Daylight Savings Time, which begins
on the first Sunday in April and ends the last Sunday in October. The restriction
would apply to construction equipment in the eight-county HGA ozone nonattainment
area of Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery,
and Waller Counties. The proposed rules would become effective April 3, 2005.
Units of state and local government within the HGA ozone nonattainment area
that have ongoing construction projects will be affected. Based on comments
received from units of state and local government affected by the DFW rules,
including the North Central Texas Council of Government (NCTCOG) and the Texas
Department of Transportation (TxDOT), costs associated with delays and extended
construction schedules may increase overall construction costs by 15% to 20%.
State and local agencies engaged in road construction and repair are anticipated
to bear the heaviest burden among state and local agencies. The proposed rules
do not require additional control equipment or new emission control technologies
to be applied to the affected diesel equipment.
The proposed rules would establish a limitation on the use of heavy-duty
diesel construction equipment as an air pollution control strategy to delay
the emission of NO
x
until later in the day, thus
limiting ozone production. The commission is required to submit a SIP revision
by the end of 2000 which will bring the HGA into attainment by 2007. The rules
proposed for HGA in this notice are one element of the ozone attainment demonstration
SIP for HGA. The purpose of the proposed rules is for the HGA nonattainment
area to demonstrate attainment with the ozone NAAQS. The SIP sets forth a
control strategy that provides part of the emission reductions necessary for
attainment and maintenance of the ozone NAAQS.
As established in the DFW rules concerning restrictions on the operation
of construction equipment, the existing rules contain exemptions from control
and recordkeeping requirements. These exemptions include construction equipment
used exclusively for emergency operations to protect public health and the
environment, and for mixing, transporting, pouring, or processing wet concrete.
Also, the existing rules contain an exemption that allows operators that submit
a plan by May 31, 2002, which is approved by the executive director and the
EPA by May 31, 2003, to operate during the restricted hours.
Units of state and local government within the HGA ozone nonattainment
area that have ongoing construction projects may have significant fiscal implications.
According to TxDOT, the TxDOT's Houston and Beaumont districts (which cover
Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and
Waller Counties) spent over $464 million during calendar year 1999 for road
and bridge construction projects in the HGA area. Based on the TxDOT expenditures,
an estimated 15% to 20% cost increase due to delays and extended construction
schedules would add $70 million to $93 million annually to TxDOT-related construction
costs in the HGA area. Note, these figures only apply to TxDOT-related road
and bridge construction costs. Because the proposed rules do not require additional
control equipment or new technology, the commission does not anticipate significant
economic impacts to affected agencies and businesses beyond the shift in work
schedule and possible implications caused by potential construction delays
attributable to the proposed rules. Delaying use of diesel construction equipment
until after noon may require affected state and local agencies and associated
businesses to adjust their work schedules and could cause extensions of construction
timelines. The fiscal impact of potential delays would depend on the scope,
magnitude, and time-critical nature of the construction projects.
PUBLIC BENEFIT AND COSTS
Mr. Davis also determined that for each year of the first five years the
proposed rules are in effect, the public benefit anticipated from enforcement
of and compliance with the proposed rules will be a potential reduction in
the formation of ozone by delaying NO
x
emissions
from construction equipment until later in the day when optimum conditions
for the formation of ozone no longer exist, potentially improved air quality,
and contribution toward demonstration of attainment with the ozone NAAQS.
The proposed rules would restrict the use of heavy-duty diesel construction
equipment, rated at 50 hp and greater, from use between the hours of 6:00
a.m. and noon, during Daylight Savings Time, which begins on the first Sunday
in April and ends the last Sunday in October. The restriction would apply
to construction equipment in the eight-county HGA ozone nonattainment area.
The proposed rules would become effective April 3, 2005.
Businesses within the HGA ozone nonattainment area that have ongoing construction
projects may have significant fiscal implications in an amount that cannot
be determined at this time; however, based on comments received from units
of state and local government affected by the DFW rules, including the NCTCOG
and TxDOT, costs associated with delays and extended construction schedules
may increase overall construction costs by 15% to 20%. Because the proposed
rules do not require additional control equipment or new technology, the commission
does not anticipate significant economic impacts to affected agencies and
businesses beyond the shift in work schedule and possible implications caused
by potential construction delays attributable to the proposed rules. Delaying
use of diesel construction equipment until after noon may require affected
state and local agencies and businesses to adjust their work schedules and
could cause extensions of construction timelines. The fiscal impact of potential
delays would depend on the scope, magnitude, the slack time available in the
schedule, and the time-critical nature of certain parts of the construction
project.
As established in the DFW rules concerning restrictions on the operation
of construction equipment, the existing rules contain exemptions from control
and recordkeeping requirements. These exemptions include construction equipment
used exclusively for emergency operations to protect public health and the
environment, and for mixing, transporting, pouring, or processing wet concrete.
Also, the existing rules contain an exemption that allows operators that submit
a plan by May 31, 2002, which is approved by the executive director and EPA
by May 31, 2003, to operate during the restricted hours.
SMALL BUSINESS AND MICRO-BUSINESS ASSESSMENT
Small and micro-businesses within the HGA ozone nonattainment area that
have ongoing construction projects may have significant fiscal implications
as a result of enforcement and administration of the proposed rules in an
amount which cannot be determined.
The proposed rules would restrict the use of heavy-duty diesel construction
equipment, rated at 50 hp and greater, from use between the hours of 6:00
a.m. and noon, during Daylight Savings Time, which begins on the first Sunday
in April and ends the last Sunday in October. The restriction would apply
to construction equipment in the eight-county HGA ozone nonattainment area.
The proposed rules would become effective April 3, 2005.
Small and micro-businesses within the HGA ozone nonattainment area that
have ongoing construction projects may have significant fiscal implications
in an amount that cannot be determined at this time; however, based on comments
received from units of state and local government affected by the DFW rules,
including the NCTCOG and TxDOT, costs associated with delays and extended
construction schedules may increase overall construction costs by 15% to 20%.
Because the proposed rules do not require additional control equipment or
new technology, the commission does not anticipate significant economic impacts
to affected small and micro-businesses beyond the shift in work schedule and
possible implications caused by potential construction delays attributable
to the proposed rules. Delaying use of diesel construction equipment until
after noon may require affected small and micro-businesses to adjust their
work schedules and could cause extensions of construction timelines. The fiscal
impact of potential delays would depend on the scope, magnitude, the slack
time available in the schedule, and the time-critical nature of certain parts
of the construction project.
As established in the DFW rule concerning restrictions on the operation
of construction equipment, the existing rules contain exemptions from control
and recordkeeping requirements. These exemptions include construction equipment
used exclusively for emergency operations to protect public health and the
environment, and for mixing, transporting, pouring, or processing wet concrete.
Also, the existing rules contain an exemption that allows operators that submit
an emissions reduction plan (plan) by May 31, 2002, which is approved by the
executive director and the EPA by May 31, 2003, to operate during the restricted
hours.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the proposed rulemaking in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225, and determined
that the rulemaking is subject to §2001.0225 because it 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 proposed rules are intended to protect
the environment or reduce risks to human health from environmental exposure
to ozone and, although we do not have definitive cost estimates at this time,
construction delays could affect a sector of the economy in a material way.
The proposed rules are intended to implement an operating-use restriction
program requiring that heavy-duty diesel construction equipment be restricted
from use between the hours of 6:00 a.m. and noon, during Daylight Savings
Time, which begins on the first Sunday in April and ends the last Sunday in
October. This program is part of the strategy to reduce the formation of ozone
by delaying NO
x
emissions from construction 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 proposed
rules are one element of the HGA Post-1999 ROP/Attainment Demonstration SIP.
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. 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 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. Thus, while specific measures are not generally required, the
emission reductions are required. 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.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code was amended by Senate Bill 633 (SB 633) during the
75th Legislative Session, 1999. The intent of SB 633 was to require agencies
to conduct a regulatory impact analysis (RIA) of extraordinary rules. These
are identified in the statutory language as 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. 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. For these reasons, rules proposed for
inclusion in the SIP fall under 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
reductions, such as those 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 obtain NO
x
emission reductions which 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 rulemaking does not exceed a standard
set by federal law, exceed an express requirement of state law (unless specifically
required by federal law), or exceed a requirement of a delegation agreement.
The rulemaking was not developed solely under the general powers of the agency,
but was specifically developed to meet the NAAQS established under federal
law and authorized under Texas Clean Air Act (TCAA), §§382.011,
382.012, 382.017, 382.019, and 382.039.
The commission invites public comment on the draft regulatory impact analysis.
TAKINGS IMPACT ASSESSMENT
The commission prepared a takings impact assessment for these rules in
accordance with Texas Government Code, §2007.043. The following is a
summary of that assessment. The specific purpose of the rulemaking action
is to establish a construction equipment operating restriction to delay NO
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that the proposed 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 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.
Interested persons may submit comments on the consistency of the proposed
rules with the CMP during the public comment period.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic
Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central
Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite
200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource
Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin.
The hearings are structured for the receipt of oral or written comments by
interested persons. Registration will begin one hour prior to each hearing.
Individuals may present oral statements when called upon in order of registration.
A four-minute time limit will be established at each hearing to assure that
enough time is allowed for every interested person to speak. Open discussion
will not occur during each hearing; however, agency staff members will be
available to discuss the proposal one hour before each hearing, and will answer
questions before and after each hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend a hearing, should contact the Office of
Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, faxed to (512) 239-4808,
or emailed to
siprules@tnrcc.state.tx.us
.
All comments should reference Rule Log Number 2000-011B-114-A1. Comments must
be received by 5:00 p.m., September 25, 2000. For further information, please
contact Gayla McCarty at (512) 239-4631 or Alan Henderson at (512) 239-1510.
STATUTORY AUTHORITY
The new sections are proposed 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 proposed 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.
The proposed new sections implement TCAA, §382.002, relating to Policy
and Purpose; §382.011, relating to General Powers and Duties; §382.012,
relating to State Air Control Plan; §382.019, relating to Methods Used
to Control and Reduce Emissions from Land Vehicles; and §382.039, relating
to Attainment Program.
§114.482.Control Requirements.
No person shall start or operate any non-road diesel construction equipment,
of 50 horsepower and above, between the hours of 6:00 a.m. and noon, during
Daylight Savings Time, which begins on the first Sunday in April and ends
on the last Sunday in October, 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 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 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 equipment are exempt
from §114.482 and §114.486 of this title (relating to Control Requirements;
and Recordkeeping 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; and
(2)
equipment used for mixing, transporting, pouring, or processing
of wet concrete provided such equipment is actually processing wet concrete.
(b)
Operators that submit an emissions reduction plan by May
31, 2002 (that is approved by the executive director and the EPA by May 31,
2003) will be exempt upon implementation of the rule in 2005, and will be
permitted to operate during the restricted hours. In order to be approved,
the plan must demonstrate reductions of oxides of nitrogen equivalent to those
required by both §114.472 of this title (relating to Control Requirements)
and §114.482 of this title, and must contain adequate enforcement provisions.
§114.489.Affected Counties and Compliance Dates.
Effective April 3, 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, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery,
and Waller Counties.
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005616
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
1.
MOTOR VEHICLE IDLING LIMITATIONS
30 TAC §§114.500, 114.502, 114.507, 114.509
The Texas Natural Resource Conservation Commission (commission)
proposes new §114.500, Definitions; §114.502, Control Requirements
for Motor Vehicle Idling; §114.507, Exemptions; and §114.509, Affected
Counties and Compliance Dates. The commission proposes these new sections
to Chapter 114, Control of Air Pollution From Motor Vehicles; new Subchapter
J, Operational Controls for Motor Vehicles; new Division 1, Motor Vehicle
Idling Restrictions; and corresponding revisions to the state implementation
plan (SIP) in order to control ground-level ozone in the Houston/Galveston
(HGA) ozone nonattainment area.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED 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. 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
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, 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 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 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 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 included in
this proposal indicates a gap of an additional 77.98 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 0.92 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 have formally submitted a resolution to
the commission, requesting the inclusion of many specific emission reduction
strategies.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses 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 proposed rules are one element of the control strategy for the HGA
Attainment Demonstration SIP. The purpose of these proposed rules is to establish
heavy-duty motor vehicle idling restrictions as one element of an air pollution
control strategy in the eight counties of the HGA ozone nonattainment area
to reduce NO
x
necessary for the counties to be
able to demonstrate attainment with the ozone NAAQS.
These proposed rules will implement idling limits for gasoline and diesel
powered engines in heavy-duty motor vehicles in the HGA area. The proposed
idling limits will lower NO
x
emissions and other
pollutants from fuel combustion. Because NO
x
is a precursor to ground-level ozone formation, reduced emissions of NO
The commission developed an ozone control strategy which limits the time
allowed for the engines of heavy-duty motor vehicles to idle when not in motion.
Currently, there are no federal regulations governing idle time for heavy-duty
motor vehicles. Therefore, the state has the authority to control motor vehicle
idling and the proposed idling requirements developed by the commission for
this NO
x
emission reduction strategy will result
in restrictions on the time allowed for motor vehicle idling.
Modeling assessing the benefits of this NO
x
emission reduction strategy demonstrated that emission reductions could be
achieved by limiting the idling time of heavy-duty motor vehicles. By the
year 2007, the idling limits will reduce NO
x
emissions in the affected area by 0.92 tpd. The commission estimates the daily
cost savings benefit of this strategy to be approximately $126,150 per ton
of NO
x
reduced. This figure was calculated from
the estimated NO
x
reductions from this strategy
of 0.92 tpd, the estimated reduction in fuel consumption per hour, and the
current price per gallon of fuel sold in the affected area.
The commission solicits 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.
SECTION BY SECTION DISCUSSION
The proposed new §114.500 contains the definitions of idle, motor
vehicle, and primary propulsion engine.
The proposed new §114.502 establishes the control requirements that
limit motor vehicle idling to five consecutive minutes when the vehicle is
not in motion during the time from April 1 through October 31.
The proposed new §114.507 provides exemptions to the control requirements
of §114.502 for motor vehicles that have a gross vehicle weight rating
of 14,000 pounds or less, that are forced to remain motionless because of
traffic conditions over which the operator has no control; are being used
as an emergency or law enforcement motor vehicle; or when the engine of a
motor vehicle is providing power takeoff for refrigeration, lift gate pumps
or other auxiliary uses; or when the engine of a motor vehicle is being operated
for maintenance or diagnostic purposes; or when the engine of a motor vehicle
is being operated solely to defrost a windshield.
The proposed new §114.509 establishes a compliance date of April 1,
2001, and identifies the eight HGA counties covered by the motor vehicle idle
control requirements of §114.502.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT
John Davis, Technical Specialist with Strategic Planning and Appropriations,
determined that for the first five-year period the proposed rules are in effect
there will be no significant fiscal implications for any single unit of state
and local government as a result of administration or enforcement of these
proposed rules.
The proposed rules will implement idling limits for state and local government
owned and operated gasoline and diesel powered engines in heavy-duty motor
vehicles with a gross vehicle weight rating (GVWR) greater than 14,000 pounds
in the HGA ozone nonattainment area. The proposed rules would affect approximately
3,200 state and local government and 92,718 privately-owned or operated gas
and diesel powered heavy-duty vehicles registered in the HGA ozone nonattainment
area. To comply with the motor vehicle idling regulations, the primary propulsion
engine for any state and local government owned and operated heavy-duty vehicle
operating in the HGA nonattainment area must not be allowed to idle for more
than five consecutive minutes when the vehicle is not in motion during the
period of April 1 through October 31 of each calendar year.
The proposed rules will implement idling limits for gasoline and diesel
powered engines in heavy-duty motor vehicles with a GVWR greater than 14,000
pounds in the HGA ozone nonattainment area. Exemptions to these proposed rules
include the following: vehicles with a GVWR of 14,000 pounds or less; vehicles
that are forced to remain motionless because of traffic conditions over which
the operator has no control; vehicles that are being used as an emergency
or law enforcement motor vehicle; when the primary propulsion engine is providing
power takeoff for refrigeration, lift gate pumps or other auxiliary uses;
when the primary propulsion engine is being operated for maintenance or diagnostic
purposes; or when the primary propulsion engine is being operated solely to
defrost a windshield.
There will be no significant fiscal impacts to units of state and local
government as a result of administration or enforcement of the proposed rules;
however, adhering to the proposed idling restrictions could provide cost savings
by reducing fuel consumption. Heavy-duty diesel and gasoline powered vehicles
can consume up to one gallon of fuel per hour while idling. The Eastern Research
Group (ERG) conducted a study titled
Determination
of NO
x
Benefits from Proposed Idle Shut-Off Rule
, July 2000, to determine the benefits of idle restrictions. Assuming
two five-minute idle periods per day, approximately 88 hours of idle time
could be saved per diesel and gasoline vehicle per year, resulting in a cost
savings of approximately $132 per vehicle per year. There are approximately
3,200 state and local government gas and diesel powered heavy-duty vehicles
registered in the HGA ozone nonattainment area. The commission anticipates
that the total annual savings to units of state and local government in the
HGA ozone nonattainment area will be approximately $422,400.
PUBLIC BENEFIT AND COSTS
Mr. Davis also determined that for the first five years the proposed rules
are in effect, the public benefit anticipated from enforcement of and compliance
with the proposed rules will be the potential reduction of NO
x
, which contributes to the formation of ground-level ozone, potentially
improved air quality, and contribution toward demonstration of attainment
with the NAAQS for the HGA ozone nonattainment area. There are no significant
fiscal implications as a result of administration or enforcement of the proposed
rules for any single person or business which owns and operates heavy-duty
gasoline and diesel vehicles within the HGA ozone nonattainment area.
The proposed rules will implement idling limits for privately-owned and
operated gasoline and diesel powered engines in heavy-duty motor vehicles
with a gross vehicle weight rating greater than 14,000 pounds in the HGA nonattainment
area. To comply with the motor vehicle idling regulations, the primary propulsion
engine for any person or business-owned and operated heavy-duty vehicle operating
in the HGA nonattainment area must not be allowed to idle for more than five
consecutive minutes when the vehicle is not in motion during the period of
April 1 through October 31 of each calendar year. Exemptions to this rule
affecting persons and businesses are the same as those described in the Cost
to State and Local Government section of this fiscal note.
There will be no significant fiscal impacts to any person or business as
a result of administration or enforcement of the proposed rules; however,
adhering to the proposed idling restrictions could provide cost savings by
reducing fuel consumption. Heavy-duty diesel and gasoline powered vehicles
can consume up to one gallon of fuel per hour while idling. The ERG conducted
a study titled
Determination of NO
x
Benefits from Proposed Idle Shut-Off Rule
, in July 2000 to
determine the benefits of idle restrictions. Assuming two five-minute idle
periods per day, approximately 88 hours of idle time could be saved per vehicle
per year, resulting in a cost savings of approximately $132 per vehicle per
year. There are approximately 92,718 privately-owned and operated gas and
diesel powered heavy-duty vehicles registered in the HGA ozone nonattainment
area. It is anticipated that the total annual savings to persons and businesses
in the HGA ozone nonattainment area will be approximately $12 million.
SMALL AND MICRO-BUSINESS ASSESSMENT
No significant adverse effects are anticipated to small or micro-businesses
as a result of implementing the proposed rules. The proposed rules will implement
idling limits for small and micro- business owned and operated gasoline and
diesel powered engines in heavy-duty motor vehicles with a gross vehicle weight
rating greater than 14,000 pounds in the HGA nonattainment area. To comply
with the motor vehicle idling regulations, the primary propulsion engine for
any persons or business- owned and operated heavy-duty vehicle operating in
the HGA nonattainment area must not be allowed to idle for more than five
consecutive minutes when the vehicle is not in motion during the period of
April 1 through October 31 of each calendar year.
There will be no significant fiscal impacts to any small or micro-business
as a result of administration or enforcement of the proposed rules; however,
adhering to the proposed idling restrictions could provide cost savings by
reducing fuel consumption. Heavy-duty diesel and gasoline powered vehicles
can consume up to one gallon of fuel per hour while idling. The ERG conducted
a study titled
Determination of NO
x
Benefits from Proposed Idle Shut-Off Rule
, in July 2000 to
determine the benefits of idle restrictions. Assuming two five-minute idle
periods per day, approximately 88 hours of idle time could be saved per vehicle
per year, resulting in a cost savings of approximately $132 per vehicle per
year. Of the 92,718 privately-owned and operated gas and diesel powered heavy-duty
vehicles registered in the HGA ozone nonattainment area, some of these vehicles
are owned by small or micro-businesses. The total savings to small and micro-businesses
would depend on the number of heavy-duty vehicles owned and operated.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the proposed rulemaking in light of the regulatory
analysis requirements of Texas Government Code, §2001.0225, and determined
that the proposed rulemaking is not subject to §2001.0225 because it
does not meet 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. The
proposed new sections to Chapter 114 are intended to protect the environment
or reduce risks to human health from environmental exposure to ozone but the
proposed control requirements within this proposal should not adversely affect
in any 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 proposed rules are intended to implement heavy-duty motor
vehicle idle limitations as part of the strategy to reduce emissions of NO
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code was amended by Senate Bill 633 (SB 633) during the
75th Legislative Session, 1999. The intent of SB 633 was to require agencies
to conduct a regulatory impact analysis (RIA) of extraordinary rules. These
are identified in the statutory language as 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. 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. For these reasons, rules proposed for
inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a),
because they are required by federal law.
Specifically, the motor vehicle idle requirements within these proposed
rules were developed in order to meet the ozone NAAQS set by the EPA under
42 USC, §7409, and therefore meet a federal requirement. States are primarily
responsible for ensuring attainment and maintenance of NAAQS once the EPA
has established those standards. Under 42 USC, §7410 and related provisions,
states must submit, for EPA approval, SIPs that provide for the attainment
and maintenance of NAAQS through a control program directed to sources of
the pollutants involved. These proposed rules are not an express requirement
of state law, but were developed specifically in order to meet the air quality
standards established under federal law as NAAQS. These proposed rules are
intended to help bring ozone nonattainment areas into compliance and to help
keep attainment and near nonattainment areas from reaching nonattainment.
The proposed rules do not exceed a standard set by federal law, exceed an
express requirement of state law unless specifically required by federal law,
nor exceed a requirement of a delegation agreement. The proposed rules were
not developed solely under the general powers of the agency, but were specifically
developed to meet the air quality standards established under federal law
as NAAQS.
The commission invites public comment on the draft regulatory impact analysis.
TAKINGS IMPACT ASSESSMENT
The commission prepared a takings impact assessment for these proposed
rules in accordance with Texas Government Code, §2007.043. The following
is a summary of that assessment. The specific purpose of the proposed rulemaking
is to establish motor vehicle idle limits which will act as an air pollution
control strategy to reduce NO
x
emissions necessary
for the eight- county HGA ozone nonattainment area to be able to demonstrate
attainment with the ozone NAAQS. Promulgation and enforcement of the proposed
rules should not burden private, real property because this proposed rulemaking
action should not result in any increased costs. Although the proposed 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 emission limitations and control requirements within this
proposal have been 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 the proposed
rules is to implement motor vehicle idle limits which are necessary for the
HGA ozone nonattainment areas to meet the air quality standards established
under federal law as NAAQS. Consequently, the exemption which applies to these
proposed rules is that of an action reasonably taken to fulfill an obligation
mandated by federal law; therefore, these proposed rules do not constitute
a takings under the Texas Government Code, Chapter 2007.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that the proposed 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 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 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.
Interested persons may submit comments on the consistency of the proposed
rules with the CMP during the public comment period.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic
Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central
Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite
200, Arlington; and September 25, 2000, 10:00 a.m., TNRCC, 12100 North I-35,
Building E, Room 201S, Austin. The hearings are structured for the receipt
of oral or written comments by interested persons. Registration will begin
one hour prior to each hearing. Individuals may present oral statements when
called upon in order of registration. A four-minute time limit will be established
at each hearing to assure that enough time is allowed for every interested
person to speak. Open discussion will not occur during each hearing; however,
agency staff members will be available to discuss the proposal one hour before
each hearing, and will answer questions before and after each hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend a hearing, should contact the Office of
Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087,
faxed to (512) 239- 4808, or emailed to
siprules@tnrcc.state.tx.us
. All comments should reference Rule Log Number 2000-011N-114-AI. Comments
must be received by 5:00 p.m., September 25, 2000. For further information,
please contact Scott Carpenter at (512) 239-1757 or Alan Henderson at (512)
239- 1510.
STATUTORY AUTHORITY
The new sections are proposed 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 the Texas Health and Safety Code,
TCAA, §382.017, which provides the commission authority to adopt rules
consistent with the policy and purposes of the TCAA. The new sections are
also proposed 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.
The proposed new sections implement TCAA, §382.002, relating to Policy
and Purpose; §382.011, relating to General Powers and Duties; §382.012,
relating to State Air Control Plan; §382.019, relating to Methods Used
to Control and Reduce Emissions from Land Vehicles; and §382.039, relating
to Attainment Program.
§114.500.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); §101.1
of this title (relating to Definitions); and §114.1 of this title (relating
to Definitions), the following words and terms, when used in this subchapter
shall have the following meanings, unless the context clearly indicates otherwise.
(1)
Idle - The operation of an engine in the operating mode
where the engine is not engaged in gear, where the engine operates at a speed
at the revolutions per minute specified by the engine or vehicle manufacturer
for when the accelerator is fully released, and there is no load on the engine.
(2)
Motor vehicle - Any self-propelled device powered by an
internal combustion engine and designed to operate with four or more wheels
in contact with the ground, 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).
(3)
Primary propulsion engine - The internal combustion engine
attached to a motor vehicle that provides the power to propel the motor vehicle
into and maintain motion.
§114.502.Control Requirements for Motor Vehicle Idling.
No person shall cause, suffer, allow, or permit the primary propulsion
engine of a motor vehicle to idle for more than five consecutive minutes in
the counties listed in §114.509 of this title (relating to Affected Counties
and Compliance Dates) when the vehicle is not in motion during the period
of April 1 through October 31 of each calendar year.
§114.507.Exemptions.
The provisions of §114.502 of this title (relating to Control
Requirements for Motor Vehicle Idling) shall not apply to:
(1)
a motor vehicle that has a gross vehicle weight rating
of 14,000 pounds or less;
(2)
a motor vehicle forced to remain motionless because of
traffic conditions over which the operator has no control;
(3)
a motor vehicle being used as an emergency or law enforcement
motor vehicle;
(4)
the primary propulsion engine of a motor vehicle providing
power takeoff for refrigeration, lift gate pumps or other auxiliary uses;
(5)
the primary propulsion engine of a motor vehicle being
operated for maintenance or diagnostic purposes; or
(6)
the primary propulsion engine of a motor vehicle being
operated solely to defrost a windshield.
§114.509.Affected Counties and Compliance Dates.
Beginning April 1, 2001, all affected persons in the following counties
shall comply with §114.502 of this title (relating to Control Requirements):
Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and
Waller.
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005628
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
The Texas Natural Resource Conservation Commission (TNRCC or commission)
proposes amendments to §§115.161, 115.162, 115.164 - 115.167, and
115.169, concerning Batch Processes; §§115.122, 115.125 - 115.127,
and 115.129, concerning Vent Gas Control; and §115.449, concerning Offset
Lithographic Printing. The commission proposes these revisions to Chapter
115, concerning Control of Air Pollution from Volatile Organic Compounds,
and to the state implementation plan (SIP) in order to conform with the United
States Environmental Protection Agency's (EPA) reasonably available control
technology (RACT) requirements in the Houston/ Galveston (HGA) ozone nonattainment
area and to obtain volatile organic compound (VOC) emission reductions which
will result in reductions in ozone formation in HGA. In an effort to improve
implementation of the existing Chapter 115, the commission also proposes amendments
to §115.10, concerning Definitions; and §§115.211, 115.212,
and 115.216, concerning Loading and Unloading of Volatile Organic Compounds;
new §115.120, concerning Vent Gas Definitions; §115.240, concerning
Stage II Vapor Recovery Definitions; and §115.430, concerning Flexographic
and Rotogravure Printing Definitions; and revisions to the SIP.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES
The HGA ozone nonattainment area is classified as Severe-17 under the 1990
Amendments to the Federal Clean Air Act (FCAA), and therefore is required
to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November
15, 2007. 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 the FCAA. 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 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 the FCAA (42 United States Code (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 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 Coastal Oxidant Assessment
for Southeast Texas (COAST) study. The commission 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. This modeling has been ongoing since that time.
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 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 one-hour 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 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 commission 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 include 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 incorporate the estimated
reductions in emissions that are 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 this 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.
Decisions regarding the actual control strategy to be submitted to the EPA
will be the next step in an iterative process of evaluating potential control
strategies, an effort which will continue through 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 HGA Attainment Demonstration SIP revision which was adopted April 19,
2000, 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
The Houston nonattainment area will need to ultimately reduce NO
x
more than 750 tons per day (tpd) to reach attainment with the one-hour
standard. In addition, a VOC reduction of about 25% will have to be achieved.
Adoption of VOC RACT rules can contribute to attainment and maintenance of
the one-hour ozone standard in the HGA area. The VOC RACT rules also may contribute
to a successful demonstration of transportation conformity in the HGA area.
Under 42 USC, §7511b of the 1990 Amendments to the FCAA, the EPA is
required to issue Control Techniques Guideline (CTG) guidance documents for
the purpose of assisting states in developing RACT controls for sources of
VOC emissions. In turn, each state is required to submit a revision to its
SIP which implements RACT regulations for VOC sources in moderate or above
ozone nonattainment areas. Specifically, FCAA, 42 USC, §7511a(b)(2)(A),
requires states to submit RACT regulations for VOC sources that are covered
by a CTG issued after November 15, 1990 (the enactment date of the 1990 FCAA),
but prior to the time of attainment. Similarly, FCAA, 42 USC, §7511a(b)(2)(C),
requires that RACT be applied to major VOC sources located in moderate or
above ozone nonattainment areas which are not the subject of a CTG; such sources
are known as "non-CTG" sources. Limits in state rules must be at least as
stringent as the CTG limits or otherwise must be determined to meet RACT.
Each CTG contains a "presumptive norm" for RACT for a specific source category,
based on the EPA's evaluation of the capabilities and problems general to
that category. Where applicable, the EPA recommends that states adopt requirements
consistent with the presumptive norm. However, the presumptive norm is only
a recommendation. States may choose to develop their own RACT requirements
on a case-by-case basis, considering the emission reductions needed to obtain
achievement of the NAAQS and the economic and technical circumstances of the
individual source.
Source categories for which the EPA was to issue CTGs under FCAA, 42 USC, §7511a(b)(2)(A),
include batch processes and offset lithographic printing. Instead of issuing
CTGs for these source categories, the EPA issued guidance documents known
as Alternative Control Techniques (ACT) documents. An ACT does not establish
the presumptive norm for RACT but merely contains information on emissions,
controls, control options, and costs. The EPA itself has consistently noted
in the ACT documents that each ACT "...presents options only, and does not
contain a recommendation on RACT." Although the EPA has not issued the required
CTGs for batch processes and offset lithographic printing, 42 USC, §7511a(b)(2)(C)
of the 1990 FCAA Amendments still requires states to ensure that RACT is in
place for all major VOC sources in moderate and above ozone nonattainment
areas.
Historically, the commission's position has been that the existing general
vent gas rule in Chapter 115, Subchapter B: Division 2 is adequate to ensure
RACT for batch processes; however, this is difficult to demonstrate because
the necessary information for such a demonstration is not in the emissions
inventory (EI). Staff attempted to develop a demonstration of equivalency
between the existing general vent gas rule and the batch processes ACT using
the EPA's 5% rule. The EPA's "5% rule" provides a mechanism for states to
justify exemptions or cutpoints which are more lenient than the EPA's RACT
baseline. It is applied by determining the total emissions allowed by the
EPA's RACT baseline (including exemptions) and comparing this to the emissions
allowed (including exemptions) by a state regulation. If the difference is
less than 5.0%, the EPA considers that there is no substantive difference
between the EPA and state requirements. The staff was unable to assemble the
information necessary to demonstrate to the EPA's satisfaction that existing
rules represent RACT for batch processes in HGA. Consequently, it is necessary
to adopt and implement Chapter 115 rules for batch processes in HGA.
Bakeries are a non-CTG source category. The EPA published an ACT guidance
document detailing appropriate control technology for bakeries. Based on this
document, as well as on input from the bakery industry, the commission developed
the applicable portion of the Chapter 115 vent gas rule pertaining to bakeries.
The EPA has stated that this rule is deficient in implementing RACT for
bakeries and therefore is unapprovable. The EPA has made it clear that failure
to correct the deficiencies will result in undesirable consequences for the
affected ozone nonattainment areas, as specified in the FCAA. The commission
adopted revisions on February 24, 1999 which address deficiencies in the bakery
rule as it applies in the Dallas/Fort Worth (DFW) ozone nonattainment area.
(See the March 12, 1999 issue of the
Texas Register
(24 TexReg 1777)). However, there are still deficiencies in the bakery
rule as it applies in HGA which must be corrected for the HGA Attainment Demonstration
SIP to be approvable. Specifically, the EPA has specified that RACT for bakery
ovens is 80-90% control efficiency, while the commission rule as negotiated
in 1994 requires only a 30% emission reduction.
The Chapter 115 offset lithographic printing rule (§§115.440,
115.442, 115.443, 115.445, 115.446, and 115.449) is currently a contingency
rule for HGA. Because HGA is a severe ozone nonattainment area, a source in
HGA is major if it has the potential to emit 25 tons per year (tpy) or more
of VOC emissions. FCAA, 42 USC, §7511a(b)(2), requires that RACT be applied
to major sources, and consequently it is necessary to implement this rule
in HGA for sources with VOC emissions equal to or greater than 25 tpy. The
rule will remain a contingency rule for offset lithographic printers in HGA
with VOC emissions below 25 tpy. The offset lithographic printers in HGA with
VOC emissions below 25 tpy must still comply with the general vent gas rules
in Chapter 115.
SECTION BY SECTION DISCUSSION
The proposed amendments to §115.10, concerning Definitions, delete
the definitions of bakery oven, synthetic organic chemical manufacturing industry
batch distillation operation, synthetic organic chemical manufacturing industry
batch process, synthetic organic chemical manufacturing industry distillation
operation, synthetic organic chemical manufacturing industry distillation
unit, and synthetic organic chemical manufacturing industry reactor process.
These terms are used solely within the Chapter 115 vent gas rules (§§115.121
- 115.123, 115.125 - 115.127, and 115.129) and are proposed to be relocated
to a new §115.120, concerning Vent Gas Definitions.
The proposed amendments to §115.10 also delete the definitions of
independent small business marketer of gasoline, and owner or operator of
a motor vehicle fuel dispensing facility. These terms are used solely within
the Chapter 115 Stage II vapor recovery rules (§§115.241 - 115.249)
and are proposed to be relocated to a new §115.240, concerning Stage
II Vapor Recovery Definitions.
In addition, the proposed amendments to §115.10 delete the definitions
of flexographic printing process, packaging rotogravure printing, publication
rotogravure printing, and rotogravure printing. These terms are used solely
within the Chapter 115 flexographic and rotogravure printing rules (§§115.432,
115.433, 115.435 - 115.437, and 115.439) and are proposed to be relocated
to a new §115.430, concerning Flexographic and Rotogravure Printing Definitions.
The proposed amendments to §115.10 also delete the definitions of
flare and vapor combustor. The definitions of these terms in §115.10
have been superceded by the corresponding definitions of these terms in 30
TAC §101.1, concerning Definitions. (See the December 17, 1999 issue
of the
Texas Register
(24 TexReg 11494)).
The commission added the definitions of flare and vapor combustor to §115.10
on June 30, 1999 as placeholders until definitions of these terms could be
added to §101.1. (See the July 16, 1999 issue of the
Texas Register
(24 TexReg 5488)).
In addition, the proposed amendments to §115.10 delete the definition
of vapor recovery system and combine it with the definition of vapor control
system. The existing definitions of vapor recovery system and vapor control
system are identical, and the commission is in the process of a transition
in the Chapter 115 rules to the term "vapor control system" from the misleading
term "vapor recovery system," which is defined to include both recovery and
combustion control devices. Combining both terms under the definition of vapor
control system will facilitate this transition.
The proposed amendments to §115.10 also revise the definitions of
external floating roof and internal floating cover to more clearly specify
that an external floating roof storage tank which is equipped with a self-supporting
fixed roof (typically a bolted aluminum geodesic dome) is considered to be
an internal floating roof storage tank for the purposes of Chapter 115 only.
In addition, the proposed amendments to §115.10 add a definition of
liquefied petroleum gas in order to clarify the exemptions in §115.217(a)(3)
and (b)(4) for loading and unloading of liquefied petroleum gas. Before the
commission adopted revisions on June 30, 1999 (effective date: July 21, 1999),
the previous versions of these exemptions referred to the safety rules of
the Liquefied Petroleum Gas Division of the Texas Railroad Commission (RRC),
which regulates many aspects of the handling and transport of liquefied petroleum
gas. Because these exemptions historically referred to the RRC rules, it follows
logically that the term "liquified petroleum gas" was intended to have the
same meaning as defined in those RRC rules (specifically, 16 TAC §9.2(32),
effective March 2, 1998). The National Fire Protection Association, which
develops and publishes fire codes and safety standards, has a definition of
liquefied petroleum gas in
Standard 58 - Standard
for the Storage and Handling of Liquefied Petroleum Gases
which is
functionally identical to the RRC's definition. Furthermore, Section 3-1 of
the
Petroleum Products Handbook
, First Edition
(Virgil B. Guthrie, editor), states that this is the most commonly used definition
of liquefied petroleum gas. Therefore, the proposed definition of liquefied
petroleum gas is consistent with other Texas state rules and industrial reference
materials.
The proposed amendments to §115.10 also revise the definition of polymer
and resin manufacturing process by replacing the "and" with "or" to make it
clear that a manufacturing process only has to manufacture a listed polymer
or a listed resin, but not both, in order to meet the definition. This proposed
amendment will make the definition consistent with the usage of this definition
in the fugitive monitoring rules for ozone nonattainment areas (§§115.352
- 115.357 and 115.359).
In addition, the proposed amendments to §115.10 revise the definition
of synthetic organic chemical manufacturing process by replacing the reference
to Table I (Synthetic Organic Chemicals) with a reference to 40 Code of Federal
Regulations (CFR) 60.489 (effective October 18, 1983). Concurrently, Table
I is being deleted. The list of affected chemicals is unchanged because Table
I was derived from the corresponding table in 40 CFR 60.489.
Finally, the proposed amendments to §115.10 revise the definition
of transport vessel to delete the ambiguous term "primarily." The revision
will clearly specify that a transport vessel includes any land-based mode
of transportation (truck or rail) of oil, gasoline, or other volatile organic
liquid bulk cargo in a storage tank which has a capacity greater than 1,000
gallons. This has always been the interpretation of the term "transport vessel,"
so this revision simply makes that interpretation more clear.
The proposed new §115.120, concerning Vent Gas Definitions, adds definitions
of bakery oven, synthetic organic chemical manufacturing industry batch distillation
operation, synthetic organic chemical manufacturing industry batch process,
synthetic organic chemical manufacturing industry distillation operation,
synthetic organic chemical manufacturing industry distillation unit, and synthetic
organic chemical manufacturing industry reactor process. These definitions
are proposed to be relocated from the §115.10, concerning Definitions,
because they are used solely within the Chapter 115 vent gas rules (§§115.121
- 115.123, 115.125 - 115.127, and 115.129).
The proposed amendments to §115.122, concerning Control Requirements,
change the 30% emission reduction requirement from the 1990 baseline emissions
inventory for major source bakeries in HGA to an 80% emission reduction requirement
from the uncontrolled VOC emission rate of the oven(s) and establish a December
31, 2001 compliance date. The proposed amendments to §115.122 also change
the baseline for major source bakeries in the DFW ozone nonattainment area
from the 1990 baseline emissions inventory to the uncontrolled VOC emission
rate of the oven(s). In addition, the proposed amendments to §115.122
update rule cross-references; update references from "standard exemption"
to "permit by rule;" and change references from "vapor recovery system" to
"vapor control system" for clarification.
The proposed amendments to §115.125, concerning Testing Requirements,
extend the existing test methods to Aransas, Bexar, Calhoun, Matagorda, San
Patricio, and Travis Counties; consolidate the existing §115.125(a) and
(b) into a single subsection; and reorganize the section by grouping related
test methods together. Because it is not reasonably possible to measure the
mass emission rate from an elevated flare (an elevated flare's flame is open
to the atmosphere, such that the emissions cannot be routed through a stack),
the test methods for flow rate and VOC concentration in the existing §115.125(a)(3)
- (6) and (b)(3) - (6), which are proposed to be renumbered as §115.125(1)
and (2), do not apply to flares. In order to specify performance requirements
for flares, the proposed revisions to new §115.125(3) establish the test
requirements of 40 CFR 60.18(b) for flares in the Beaumont/Port Arthur (BPA),
DFW, and HGA ozone nonattainment areas. Because flares cannot be stack-tested,
the proposed amendments to §115.125(3) also specify that compliance with
the requirements of 40 CFR 60.18(b) represents compliance with the emission
specifications of §115.121 and the control efficiency requirements of §115.122.
In addition, the proposed amendments to §115.125 include an option that
the owner or operator of a vapor combustor may consider it to be a flare and
meet the flare requirements specified in 40 CFR 60.18(b) instead of the test
methods and procedures appropriate for a thermal or catalytic oxidizer. The
proposed amendments to §115.125 also add a new paragraph (5), which authorizes
the use of test methods other than those specifically listed in §115.125,
provided that any new test method is validated using the procedures in 40
CFR 63, Appendix A, Test Method 301, with the executive director acting as
the administrator. This revision is necessary because in some specific unique
situations, the listed test methods may be inappropriate. The new paragraph
(5) increases flexibility by allowing the use of additional test methods which
may be more cost-effective and more appropriate in certain unique situations.
The proposed amendments to §115.126, concerning Monitoring and Recordkeeping
Requirements, extend the existing test methods to Aransas, Bexar, Calhoun,
Matagorda, San Patricio, and Travis Counties; consolidate the existing §115.126(a)
and (b) into a single subsection; update references to other sections; and
replace "true partial pressure" with the more understandable term "concentration."
The proposed amendments to §115.126 also change the 30% emission reduction
requirement from the 1990 baseline emissions inventory for major source bakeries
in HGA to an 80% emission reduction requirement from the uncontrolled VOC
emission rate of the oven(s), establish a December 31, 2001 compliance date,
and require submittal of a control plan by March 31, 2001 which shows how
the owner or operator will meet the emission reduction requirements. In addition,
the proposed amendments to §115.126 change the baseline for major source
bakeries in DFW from the 1990 emissions inventory to the uncontrolled VOC
emission rate of the oven(s), and delete the annual reporting requirements
for major source bakeries in DFW and HGA. Because the major source bakeries
in DFW and HGA have installed (or are in the process of installing) catalytic
oxidizers which can readily meet the control requirements and the monitoring
and recordkeeping requirements will ensure that these control devices are
functioning properly, there is no need for these bakeries to submit an annual
report.
Finally, the proposed amendments to §115.126 also specify that flares
in BPA, DFW, and HGA must meet the requirements of 40 CFR 60.18(b) and Chapter
111; and state that records of appropriate operating parameters must be kept
for types of vapor control systems not specifically listed in §115.126(1)(A)
and (B). The proposed §115.126(1)(A)(iv) and (1)(B) specify exhaust gas
temperature monitoring of vapor combustors, with an option that the owner
or operator of a vapor combustor may consider it to be a flare and monitor
the unit under the flare requirements specified in 40 CFR 60.18(b) and 30
TAC Chapter 111. These amendments are necessary to ensure that control devices
are functioning properly and to clarify how vapor combustors are to be monitored.
Based upon information from the Air Permits Division, most existing flares
meet the design and operating criteria of 40 CFR 60.18(b). The commission
solicits information regarding vents in BPA, DFW, and HGA which are controlled
by flares that do not meet the requirements of 40 CFR 60.18(b).
Sources which are addressed by a Chapter 115 contingency rule (i.e., one
in which Chapter 115 requirements are triggered for that source by the commission
publishing notification in the
Texas Register
that implementation of the contingency rule is necessary) are subject to the
requirements of Division 2, concerning Vent Gas Control, until the compliance
date of that contingency rule. The purpose is to ensure that a Chapter 115
rule (either the general vent gas rule or the more specific contingency rule,
but not both) applies at all times to sources addressed by a contingency rule.
The proposed amendments to §115.127(a) add a new paragraph (8) which
specifies that for a source that is addressed by a Chapter 115 contingency
rule, the owner or operator of that source may choose to comply with the requirements
of the contingency rule as though the contingency rule already had been implemented
for that source, rather than complying with Division 2. In the case of bakeries,
this option would be an alternative to complying with the general vent gas
control requirements of §115.121(a)(1) and §115.122(a)(1) because
these currently applicable requirements are in the same division (Division
2, concerning Vent Gas Control), as the bakery contingency measure requirements.
For example, under §115.449(c) the offset printing rules of §§115.442
- 115.446 are a contingency rule for each printing operation in DFW for which
all offset lithographic printing presses on a property, when uncontrolled,
emit a combined weight of VOC less than 50 tons per calendar year. Such sources
are currently subject to the requirements of Division 2, concerning Vent Gas
Control. Under the proposed new §115.127(a)(8), the owner or operator
of such a printing operation instead would have the option of complying with
the offset printing rules of §§115.442 - 115.446 as though that
offset printing contingency rule had been implemented in DFW and the compliance
date had already passed.
In addition, the proposed amendments to §115.127 delete the concentration
thresholds in true partial pressure and retain the more understandable concentration
thresholds in parts per million by volume.
The proposed amendments to §115.129, concerning Counties and Compliance
Schedules, specify the compliance schedule for the new requirements described
earlier in this preamble; delete language which is obsolete due to the passing
of the May 31, 1996 and November 15, 1996 compliance dates; and update references
to other sections.
The proposed rule amendments add the Chapter 115 batch process requirements
(§§115.160 - 115.167 and 115.169) to the eight-county HGA ozone
nonattainment area. The rule language is based upon the EPA's
Control of Volatile Organic Compound Emissions from Batch Processes - Alternative
Control Techniques Information Document
(EPA-453/R-94-020, February
1994).
The proposed amendments to §115.161, concerning Applicability, specify
that the batch process requirements of §§115.162 - 115.167 apply
to vent gas streams at batch process operations in the HGA area under the
Standard Industrial Classification (SIC) codes 2821 (plastic resins and materials),
2833 (medicinals and botanicals), 2834 (pharmaceutical preparations), 2861
(gum and wood chemicals), 2865 (cyclic crudes and intermediates), 2869 (industrial
organic chemicals, not elsewhere classified), and 2879 (agricultural chemicals,
not elsewhere classified).
The proposed amendments to §115.161 also specify that the existing
requirements of Subchapter B, Division 2, concerning Vent Gas Control, will
continue to apply to batch process operations in HGA which are exempt from §§115.162
- 115.166 because they are located at an account which has total VOC emissions
(determined before control but after the last recovery device) of less than
25 tpy from all stationary emission sources at the account.
The proposed amendments to §115.162, concerning Control Requirements,
make batch process operations in HGA subject to: the applicable RACT equations
for low, moderate, and high volatility materials; a successive ranking scheme
which determines which sources must be controlled and which are exempt; and
the EPA's "once-in, always-in" (OIAI) requirement. OIAI is an EPA concept
which means that once emissions from a source exceed the applicability cutoff
for a particular VOC regulation in the SIP, that source is always subject
to the control requirements of the regulation.
Although no amendments are proposed to §115.163, concerning Alternate
Control Requirements, an alternate means of control will be available under
this section for batch process operations in HGA.
The proposed amendments to §115.164, concerning Determination of Emissions
and Flow Rates, make batch process operations in HGA subject to the procedures
for determining the uncontrolled annual emission total and the average flow
rate for process vents.
The proposed amendments to §115.165, concerning Approved Test Methods
and Testing Requirements, make batch process operations in HGA subject to
specified test methods and testing requirements for determining compliance
with the control requirements. Minor modifications to the test methods may
be used if approved by the executive director.
Because it is not reasonably possible to measure the mass emission rate
from an elevated flare (an elevated flare's flame is open to the atmosphere,
such that the emissions cannot be routed through a stack), the test methods
for flow rate and VOC concentration do not apply to flares. In order to specify
performance requirements for flares, §115.165 includes the test requirements
of 40 CFR 60.18(b). Because flares cannot be stack-tested, the §115.165
also specifies that compliance with the requirements of 40 CFR 60.18(b) represents
a 98% control efficiency. Based upon information from the Air Permits Division,
most existing flares meet the design and operating criteria of 40 CFR 60.18(b).
The commission solicits information regarding flares which are used to control
emissions from batch process operations in HGA, but do not meet the requirements
of 40 CFR 60.18(b).
Section 115.165 also includes authorization for the use of test methods
other than those specifically listed in §115.165, provided that any new
test method is validated using the procedures in 40 CFR 63, Appendix A, Test
Method 301, with the executive director acting as the administrator. This
option is included in §115.165 because in some specific unique situations
the listed test methods may be inappropriate. The availability of this option
increases flexibility by allowing the use of additional test methods which
may be more cost-effective and more appropriate in certain unique situations.
The proposed amendments to §115.166, concerning Recordkeeping Requirements,
make batch process operations in HGA subject to requirements for: continuous
monitoring and recording of control device operating parameters; recordkeeping
of the annual mass emission total, average flow rate, and associated documentation
for each process vent; and the control device operating parameters to be measured
and recorded during performance testing. The proposed amendments also change
an incorrect reference in §115.166(1) from "VOC transfer operations"
to "batch process operations." As a result of this correction, the term "VOC"
is being spelled out in §115.166(1)(A)(iii)(II).
The proposed amendments to §115.167, concerning Exemptions, make the
following exemptions available in HGA: batch process operations which are
located at an account in HGA which has total VOC emissions (determined before
control but after the last recovery device) of less than 25 tpy; single unit
operations that have a mass annual emissions of 500 pounds per year or less;
and combined vents from a batch process train which have a mass annual emissions
total below specified levels which vary depending on the volatility of the
VOCs. In addition, the proposed amendments revise the existing exemption in §115.167(2)
to clarify that §115.164, concerning Determination of Emissions and Flow
Rates, is to be used for determining if the exemptions available under §115.167(2)
are met. The proposed amendments to §115.167 also specify that the existing
requirements of Subchapter B, Division 2, concerning Vent Gas Control, will
continue to apply to batch process operations which qualify for exemption
because they are located at an account in HGA which has total VOC emissions
(determined before control but after the last recovery device) of less than
25 tpy.
The proposed amendments to §115.169, concerning Counties and Compliance
Schedules, specify the newly affected counties in HGA (Brazoria, Chambers,
Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller) and a December
31, 2002 compliance date for the new requirements. The proposed amendments
to §115.169 also specify that batch process operations which are subject
to the requirements of §§115.162 - 115.166 must continue to comply
with the existing requirements of Subchapter B, Division 2, concerning Vent
Gas Control, until these batch process operations are in compliance with the
new requirements.
The proposed amendments to §115.211, concerning Emission Specifications,
delete a reference to gasoline bulk plants which is no longer necessary due
to the deletion of the gasoline bulk plant emission specification adopted
by the commission on November 10, 1999. (See the November 26, 1999 issue of
the
Texas Register
(24 TexReg 10559)).
The proposed amendments to §115.212, concerning Control Requirements,
revise §115.212(a)(3) and (b)(3) to state that the requirements regarding
vapor and liquid leaks during land-based VOC transfer apply specifically to
transport vessels. This revision is necessary in order to clarify that the
requirements are not intended to apply to vessels which do not meet the definition
of "transport vessel" in §115.10 (for example, drums).
The proposed amendments to §115.216, concerning Monitoring and Recordkeeping
Requirements, revise §115.216(3)(A)(i) to only require records of the
identification number of tank-truck tanks for which annual leak testing is
required under §115.214(a)(1)(C) or (b)(1)(C), rather than all tank-truck
tanks as is currently required. This amendment is being proposed because it
is unnecessary to track the identification number of tank-truck tanks which
are excluded from the annual leak testing requirements.
The proposed new §115.240, concerning Stage II Vapor Recovery Definitions,
adds definitions of independent small business marketer of gasoline, and owner
or operator of a motor vehicle fuel dispensing facility. These definitions
are proposed to be relocated from the §115.10, concerning Definitions,
because they are used solely within the Chapter 115 Stage II vapor recovery
rules (§§115.241 - 115.249).
The proposed new §115.430, concerning Flexographic and Rotogravure
Printing Definitions, adds definitions of flexographic printing process, packaging
rotogravure printing, publication rotogravure printing, and rotogravure printing.
These definitions are proposed to be relocated from the §115.10, concerning
Definitions, because they are used solely within the Chapter 115 flexographic
and rotogravure printing rules (§§115.432, 115.433, 115.435 - 115.437,
and 115.439). In addition, the commission proposes to change the title of
Subchapter E, Division 3 from "Graphic Arts (Printing) by Rotogravure and
Flexographic Processes" to "Flexographic and Rotogravure Printing" in order
to more clearly specify the operations addressed by to this division.
HGA is classified as a severe ozone nonattainment area and the major source
definition includes VOC sources with emissions of 25 tpy and higher. Because
FCAA, 42 USC, §7511a(b)(2), requires that RACT be applied to major sources,
the proposed amendments to §115.449, concerning Counties and Compliance
Schedules, implement the offset lithographic printing rule in HGA for sources
with VOC emissions equal to or greater than 25 tpy and establishes a compliance
date of December 31, 2002. The offset lithographic printing rule is currently
a contingency rule for HGA; after the proposed change, the rule will be a
contingency rule for offset lithographic printers in HGA with VOC emissions
below 25 tpy.
EFFECT ON SITES SUBJECT TO THE FEDERAL OPERATING PERMITS PROGRAM
Since 30 TAC Chapter 115 is an applicable requirement under 30 TAC Chapter
122, owners or operators subject to the Federal Operating Permit Program must,
consistent with the revision process in Chapter 122, revise their operating
permit to include the revised Chapter 115 requirements for each emission unit
affected by the revisions to Chapter 115 at their site.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT
John Davis, Technical Specialist in the Strategic Planning and Appropriations
Section, has reviewed these proposed amendments to Chapter 115, Control of
Air Pollution from Volatile Organic Compounds, under the requirements of Texas
Government Code, §2001.024, and has made the following determination
concerning the fiscal effects of the proposed amendments for each year of
the first five years the amendments are in effect.
Mr. Davis has determined that for the first five-year period the proposed
amendments to Chapter 115 are in effect, there will be no significant fiscal
implications for units of state and local government as a result of administration
or enforcement of the proposed amendments, except those that may operate sources
subject to the proposed revisions to Chapter 115. For these units of state
and local government, the fiscal implications of these revisions to Chapter
115 will be equivalent to those for any affected public or private entity.
Most of the sources which will have to comply with the proposed rules are
currently subject to air permits and are already being inspected for compliance.
Consequently, only a limited number of additional facilities will need to
be inspected for compliance with the proposed Chapter 115 rule amendments.
The commission anticipates that the Field Operations Division inspectors will
inspect for compliance with the proposed requirements when conducting their
routine inspections. The commission also anticipates that enforcement of these
rules will not significantly increase the number of facilities currently inspected
by the state and local governments. However, these rules will cause a minor
increase in workload when inspecting the affected facilities.
PUBLIC BENEFIT AND COSTS
Mr. Davis has also determined that for each year of the first five years
the proposed amendments to Chapter 115 are in effect, the public benefit anticipated
from enforcement of and compliance with the proposed amendments will be: a
reduction of public exposure to VOC emitted from affected batch processes,
offset lithographic printers, and bakeries; the concomitant reduced risks
to human health and safety from ozone; a reduction of ground-level ozone in
the HGA ozone nonattainment area; and conformance with the requirements of
the FCAA.
The proposed amendments to Chapter 115 will ensure that the batch process,
offset lithographic printing, and bakery rules represent RACT in HGA, which
will satisfy FCAA requirements and enable these rules to be federally approvable.
The amendments would require these sources in the HGA ozone nonattainment
area to meet new emission specifications and other requirements in order to
reduce VOC emissions and ozone air pollution. These standards and specifications
are part of the strategy to reduce emissions of VOC necessary for the counties
in the HGA ozone nonattainment area to be able to demonstrate attainment with
the NAAQS for ozone. The proposed amendments are one element of the proposed
HGA attainment demonstration SIP. A SIP is a plan developed for any region
where existing (measured and estimated) ambient levels of pollutant exceeds
the levels specified in a national standard. The plan sets forth a control
strategy that provides emission reductions necessary for attainment and maintenance
of the national standards.
For batch processes, the commission estimates the cost-effectiveness (the
cost per ton of VOC emissions reduced), annualized total cost of control,
annual operating costs, and total capital cost for flow rates of 500 and 5,000
standard cubic feet per minute (scfm) as follows, based on the cost- effectiveness
data of Appendix F of EPA's
Control of Volatile Organic
Compound Emissions from Batch Processes - Alternative Control Techniques Information
Document
(EPA-453/R-94- 020, February 1994).
Figure: 30 TAC Chapter 115 - Preamble
For sources which route vent gas emissions (including batch process emissions)
to flares that do not already meet the requirements of 40 CFR 60.18(b), the
commission estimates the cost of testing to determine the exit velocity and
the net heating value of the vapors being combusted to be approximately $6,000,
based upon vendor estimates. The commission estimates that installing a heat-sensing
device, such as an ultraviolet beam sensor or thermocouple, at the pilot light
to indicate the continuous presence of a flame would cost approximately $19,300
to $22,300, based upon vendor estimates.
For bakeries, an analysis of the emissions inventory revealed that there
are four bakeries in HGA with VOC emissions at or above 25 tpy and four bakeries
in DFW with VOC emissions at or above 50 tpy that will become subject to the
vent gas rule's revised control requirements. These bakeries have already
installed (or are installing) catalytic oxidizers in response to previous
rulemaking. Each of these catalytic oxidizers can meet the revised control
requirements, and therefore there will be no cost to install add-on control
devices. Elimination of the annual reporting requirement will result in a
minor cost savings due to the associated reduction in manpower needed to assemble
the reports.
For offset lithographic printers, the commission estimates that there are
approximately 20 sources in HGA with VOC emissions at or above 25 tpy that
will become subject to the offset printing requirements. The printers with
offset heatset printing presses have already installed add-on controls due
to Chapter 111 opacity limitations and/or Chapter 116 new source review permitting
requirements. Because these add-on controls can already meet the control requirements,
there will be no cost for installation of add-on control devices. Regarding
the fountain solution limitations which would apply to both heatset and nonheatset
offset printing, EPA's draft
Control Techniques Guideline
for Offset Lithographic Printing
(December 14, 1992) estimates that
reducing alcohol in the fountain solution results in a savings of $920 per
ton of alcohol not used. This document states that nonalcohol fountain solutions
save money because they are used in lower quantities, even though they cost
more than alcohol. Regarding the cleaning solution limitations which would
apply to both heatset and nonheatset offset printing, the draft CTG states
that lower VOC cleaning solutions are slightly more expensive than traditional
cleaning solutions. This document estimates that the incremental costs of
using lower VOC cleaning solutions range from approximately $550 to $24,000
per year, depending on the size and type of the printing plant.
SMALL BUSINESS AND MICRO-BUSINESS ASSESSMENT
The agency has been unable to identify any small businesses or micro-businesses
as defined in the Texas Government Code which would be affected by these proposed
amendments to Chapter 115. If there are affected small businesses or micro-businesses,
the estimated annualized cost for installing and operating the control technology
in dollars per ton of VOC reduced that was used for the various types of units
in this fiscal note would appear to be a reasonable cost estimate for small
businesses or micro- businesses. The proposed amendments do not specify a
particular control technology to achieve the emission limits and there may
be other control technologies or combinations of control technologies which
may be used to comply.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission has reviewed the rulemaking 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. The amendments to Chapter 115 are one element of the HGA Attainment
Demonstration SIP and will require VOC emission reductions from batch processes,
offset lithographic printers, and bakeries in the HGA ozone nonattainment
area. While the rules are intended to protect the environment, based on the
analysis provided earlier in this preamble and in particular, the discussion
in the Public Benefit and Costs section, the commission does not believe that
the rules will adversely affect, in a material way, the operation of certain
batch processes, offset lithographic printers, and bakeries. 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.
The amendments do not meet the definition of a "major environmental rule"
as defined in the Texas Government Code, and they do not meet any of the four
applicability requirements listed in §2001.0225(a). FCAA, 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 FCAA, 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 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 FCAA, 42 USC, §7410. Thus, while specific measures
are not generally required, the emission reductions are required. States are
not free to ignore the requirements of FCAA, 42 USC, §7410, and must
develop programs to assure that the nonattainment areas of the state will
be brought into attainment on schedule.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code was amended by Senate Bill 633 (SB 633) during the
75th Legislative Session. The intent of SB 633 was to require agencies to
conduct a regulatory impact analysis (RIA) of extraordinary rules. These are
identified in the statutory language as 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. 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 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. For these reasons, rules adopted for
inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a),
because they are specifically required by federal law. FCAA, 42 USC, §7511a(b)(2)(C),
requires states to ensure that RACT is in place for all major VOC sources
in moderate and above ozone nonattainment areas. The commission has performed
photochemical grid modeling which predicts that VOC emission reductions, such
as those required by these rules, will result in reductions in ozone formation
in the HGA ozone nonattainment area. This rulemaking is not an express requirement
of state law, but was developed specifically in order to ensure that RACT
is in place for all major VOC sources in the HGA ozone nonattainment area
as required under federal law. This will enable the Chapter 115 batch process,
offset lithographic printing, and bakery rules for HGA to be federally approvable.
This rulemaking is also intended to obtain VOC emission reductions which 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 rulemaking does not exceed a standard
set by federal law, exceed an express requirement of state law (unless specifically
required by federal law), or exceed a requirement of a delegation agreement.
The rulemaking was not developed solely under the general powers of the agency,
but was specifically developed to meet the RACT requirements and NAAQS established
under federal law and authorized under Texas Clean Air Act (TCAA), §§382.011,
382.012, and 382.017.
The commission invites public comment on the draft regulatory impact analysis.
TAKINGS IMPACT ASSESSMENT
The commission has prepared a takings impact assessment for these rules
pursuant to Texas Government Code, §2007.043. The following is a summary
of that assessment. The specific purpose of the rulemaking is twofold: to
ensure that RACT is in place for all major VOC sources in the HGA ozone nonattainment
area in order to conform with the EPA's RACT requirements, thus enabling the
Chapter 115 batch process, offset lithographic printing, and bakery rules
for HGA to be federally approvable; and to obtain VOC emission reductions
which 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. This rulemaking action may require the
installation of control systems at batch process operations, offset lithographic
printers, and bakeries in HGA in some cases. Promulgation and enforcement
of the rule amendments may possibly burden private property because in some
cases the permanent installation of control systems and associated piping
is necessary in order to comply with the rules. 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 fulfill federal mandates under the 1990 Amendments to the FCAA,
42 USC, §7410 and §7511a(b)(2). Specifically, FCAA, 42 USC, §7511a(b)(2)(C),
requires states to ensure that RACT is in place for all major VOC sources
in moderate and above ozone nonattainment areas. In addition, the emission
limitations and control requirements within this rulemaking were developed
in order to meet the NAAQS for ozone set by the EPA under FCAA, 42 USC, §7409.
States are primarily responsible for ensuring attainment and maintenance of
NAAQS once the EPA has established them. Under the FCAA, 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 ensure that RACT is in place for all major VOC sources
in the HGA ozone nonattainment area as required under federal law and to meet
the air quality standards established under federal law as NAAQS. Consequently,
the following exemption applies to these rules: an action reasonably taken
to fulfill an obligation mandated by federal law.
COASTAL MANAGEMENT PROGRAM CONSISTENCY REVIEW
The commission has determined that this 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's rules in 30 TAC Chapter
281, Subchapter B, concerning Consistency with 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 has reviewed this action for consistency with the CMP
goals and policies in accordance with the regulations of the Coastal Coordination
Council. For this rulemaking, the commission has determined that the 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. This rulemaking is intended to reduce
overall emissions of VOC from batch process vent gas streams, bakeries, and
offset lithographic printers. This action is consistent with the CMP because
it does not authorize any new emissions and will reduce existing emissions
of VOC. Interested persons may submit comments on the consistency of the proposed
rules with the CMP during the public comment period.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic
Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central
Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite
200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource
Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin.
The hearings are structured for the receipt of oral or written comments by
interested persons. Registration will begin one hour prior to each hearing.
Individuals may present oral statements when called upon in order of registration.
A four-minute time limit will be established at each hearing to assure that
enough time is allowed for every interested person to speak. Open discussion
will not occur during each hearing; however, agency staff members will be
available to discuss the proposal one hour before each hearing, and will answer
questions before and after each hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend a hearing, should contact the Office of
Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087;
faxed to (512) 239- 4808; or emailed to
siprules@tnrcc.state.tx.us
. All comments should reference Rule Log Number 2000-011i-115-AI. Comments
must be received by 5:00 p.m., September 25, 2000. For further information,
please contact Eddie Mack of the Strategic Assessment Division at (512) 239-1488.
Subchapter A. DEFINITIONS
30 TAC §115.10
STATUTORY AUTHORITY
The amendment is proposed under the Texas Health and Safety Code, TCAA, §382.011,
concerning General Powers and Duties, which provides the commission with the
authority to establish the level of quality to be maintained in the state's
air and the authority to control the quality of the state's air; §382.017,
concerning Rules, which provides the commission with the authority to adopt
rules consistent with the policy and purposes of the TCAA; and §382.012,
concerning State Air Control Plan, which requires the commission to develop
plans for protection of the state's air.
The proposed amendment implements the Texas Health and Safety Code, TCAA, §§382.011,
382.012, and 382.017.
§115.10.Definitions.
Unless specifically defined in the Texas Clean Air Act (TCAA) or in
the rules of the Texas Natural Resource Conservation Commission (commission),
the terms used by the commission 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, the following terms, when used in this chapter, shall
have the following meanings, unless the context clearly indicates otherwise.
Additional definitions for terms used in this chapter are found in §101.1
of this title (relating to Definitions) and §3.2 of this title (relating
to Definitions).
[
Bakery oven - An oven for
baking bread or any other yeast-leavened products.]
(1)
[
(2)
[
(3)
[
(4)
[
(5)
[
(6)
[
(7)
[
(8)
[
(9)
[
[
Flare - An open combustor
without enclosure or shroud which is used as a control device.]
[
Flexographic printing process
- A method of printing in which the image areas are raised above the non-image
areas, and the image carrier is made of an elastomeric material.]
(10)
[
(11)
[
(12)
[
(13)
[
[
Independent small business
marketer of gasoline - A person engaged in the marketing of gasoline who owns
the dispensing equipment at a motor vehicle fuel dispensing facility and receives
at least 50% of his annual income from the marketing of gasoline. A person
is not an independent small business marketer of gasoline if such person:]
[
is a refiner; or]
[
controls (i.e., owns more than 50% of a business
or corporation's stock), is controlled by, or is under common control with,
a refiner; or]
[
is otherwise directly or indirectly affiliated
with a refiner or with a person who controls, is controlled by, or is under
common control with a refiner (unless the sole affiliation is by means of
a supply contract or an agreement or contract to use a trademark, trade name,
service mark, or other identifying symbol or name owned by such refiner or
any such person).]
(14)
[
(15)
Liquefied petroleum gas -
Any material that is composed predominantly of any of the following hydrocarbons
or mixtures of hydrocarbons: propane, propylene, normal butane, isobutane,
and butylenes.
(16)
[
(17)
[
(18)
[
(19)
[
(20)
[
[
Owner or operator of a motor
vehicle fuel dispensing facility (as used in §§115.241 - 115.249
of this title (relating to Control of Vehicle Refueling Emissions (Stage II)
at Motor Vehicle Fuel Dispensing Facilities)) - Any person who owns, leases,
operates, or controls the motor vehicle fuel dispensing facility.]
[
Packaging rotogravure printing
- Any rotogravure printing upon paper, paper board, metal foil, plastic film,
or any other substrate which is, in subsequent operations, formed into packaging
products or labels.]
(21)
[
(22)
[
(23)
[
[
Publication rotogravure printing
- Any rotogravure printing upon paper which is subsequently formed into books,
magazines, catalogues, brochures, directories, newspaper supplements, or other
types of printed materials.]
[
Rotogravure printing - The
application of words, designs, and/or pictures to any substrate by means of
a roll printing technique which involves a recessed image area. The recessed
area is loaded with ink and pressed directly to the substrate for image transfer.]
[
Synthetic Organic Chemical
Manufacturing Industry (SOCMI) batch distillation operation - A SOCMI noncontinuous
distillation operation in which a discrete quantity or batch of liquid feed
is charged into a distillation unit and distilled at one time. After the initial
charging of the liquid feed, no additional liquid is added during the distillation
operation.]
[
Synthetic Organic Chemical
Manufacturing Industry (SOCMI) batch process - Any SOCMI noncontinuous reactor
process which is not characterized by steady-state conditions, and in which
reactants are not added and products are not removed simultaneously.]
[
Synthetic Organic Chemical
Manufacturing Industry (SOCMI) distillation operation - A SOCMI operation
separating one or more feed stream(s) into two or more exit streams, each
exit stream having component concentrations different from those in the feed
stream(s). The separation is achieved by the redistribution of the components
between the liquid and vapor-phase as they approach equilibrium within the
distillation unit.]
[
Synthetic Organic Chemical
Manufacturing Industry (SOCMI) distillation unit - A SOCMI device or vessel
in which distillation operations occur, including all associated internals
(including, but not limited to, trays and packing), accessories (including,
but not limited to, reboilers, condensers, vacuum pumps, and steam jets),
and recovery devices (such as absorbers, carbon adsorbers, and condensers)
which are capable of, and used for, recovering chemicals for use, reuse, or
sale.]
[
Synthetic Organic Chemical
Manufacturing Industry (SOCMI) reactor process - A SOCMI unit operation in
which one or more chemicals, or reactants other than air, are combined or
decomposed in such a way, that their molecular structures are altered and
one or more new organic compounds are formed.]
(24)
[
(25)
[
(26)
[
(27)
[
(28)
[
[
Vapor combustor - A partially
enclosed combustion device, where the combustion flame may be partially visible,
but at no time does the device operate with a fully visible flame. A vapor
combustor is used to destroy VOCs to the destruction requirements defined
in the applicable emission specifications and control requirements sections
of this chapter by smokeless combustion without extracting energy in the form
of process heat or steam. Auxiliary fuel and/or a flame air control damping
system, which can operate at all times to control the air/fuel mixture to
the combustor's flame zone, may be required to ensure smokeless combustion
during operation.]
(29)
[
[
Vapor recovery system - Any
control system which utilizes vapor collection equipment to route VOC to a
control device that reduces VOC emissions.]
(30)
[
(31)
[
[
This agency hereby certifies that the proposal has been
reviewed by legal counsel and found to be within the agency's legal authority
to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005638
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
2.
VENT GAS CONTROL
30 TAC §§115.120, 115.122, 115.125 - 115.127, 115.129
STATUTORY AUTHORITY
The new section and amendments are proposed under the Texas Health and
Safety Code, Texas Clean Air Act (TCAA), §382.011, concerning General
Powers and Duties, which provides the commission with the authority to establish
the level of quality to be maintained in the state's air and the authority
to control the quality of the state's air; §382.017, concerning Rules,
which provides the commission with the authority to adopt rules consistent
with the policy and purposes of the TCAA; and §382.012, concerning State
Air Control Plan, which requires the commission to develop plans for protection
of the state's air.
The proposed new section and amendments implement the Texas Health and
Safety Code, TCAA, §§382.011, 382.012, and 382.017.
§115.120.Vent Gas Definitions.
The following words and terms, when used in this division, shall have
the following meanings, unless the context clearly indicates otherwise. Additional
definitions for terms used in this division are found in §115.10 of this
title (relating to Definitions), §101.1 of this title (relating to Definitions),
and §3.2 of this title (relating to Definitions).
(1)
Bakery oven - An oven for baking bread or any other yeast-leavened
products.
(2)
Synthetic Organic Chemical Manufacturing Industry (SOCMI)
batch distillation operation - A SOCMI noncontinuous distillation operation
in which a discrete quantity or batch of liquid feed is charged into a distillation
unit and distilled at one time. After the initial charging of the liquid feed,
no additional liquid is added during the distillation operation.
(3)
Synthetic Organic Chemical Manufacturing Industry (SOCMI)
batch process - Any SOCMI noncontinuous reactor process which is not characterized
by steady-state conditions, and in which reactants are not added and products
are not removed simultaneously.
(4)
Synthetic Organic Chemical Manufacturing Industry (SOCMI)
distillation operation - A SOCMI operation separating one or more feed stream(s)
into two or more exit streams, each exit stream having component concentrations
different from those in the feed stream(s). The separation is achieved by
the redistribution of the components between the liquid and vapor-phase as
they approach equilibrium within the distillation unit.
(5)
Synthetic Organic Chemical Manufacturing Industry (SOCMI)
distillation unit - A SOCMI device or vessel in which distillation operations
occur, including all associated internals (including, but not limited to,
trays and packing), accessories (including, but not limited to, reboilers,
condensers, vacuum pumps, and steam jets), and recovery devices (such as absorbers,
carbon adsorbers, and condensers) which are capable of, and used for, recovering
chemicals for use, reuse, or sale.
(6)
Synthetic Organic Chemical Manufacturing Industry (SOCMI)
reactor process - A SOCMI unit operation in which one or more chemicals, or
reactants other than air, are combined or decomposed in such a way that their
molecular structures are altered and one or more new organic compounds are
formed.
§115.122.Control Requirements.
(a)
For all persons in the Beaumont/Port Arthur, Dallas/Fort
Worth, El Paso, and Houston/Galveston areas, the following control requirements
shall apply
.
[
(1)
Any vent gas streams affected by §115.121(a)(1) of
this title (relating to Emission Specifications) must be controlled properly
with a control efficiency of at least 90% or to a volatile organic compound
(VOC) concentration of no more than 20 parts per million by volume (ppmv)
(on a dry basis corrected to 3.0% oxygen for combustion devices):
(A) - (B)
(No change.)
(C)
by any other vapor
control
[
(2)
Any vent gas streams affected by §115.121(a)(2) of
this title must be controlled properly with a control efficiency of at least
98% or to a VOC concentration of no more than 20 ppmv (on a dry basis corrected
to 3.0% oxygen for combustion devices):
(A)
(No change.)
(B)
by any other vapor
control
[
(3)
For the Dallas/Fort Worth, El Paso, and Houston/Galveston
areas, VOC emissions from each bakery with a bakery oven vent gas stream(s)
affected by §115.121(a)(3) of this title shall be reduced as follows.
(A)
Each bakery in the Houston/Galveston area with a total
weight of VOC emitted from all bakery ovens on the property, when uncontrolled,
equal to or greater than 25 tons per calendar year shall
ensure that
the overall emission reduction from the uncontrolled VOC emission rate of
the oven(s) will be
[
(B)
Each bakery in the Dallas/Fort Worth area with a total
weight of VOC emitted from all bakery ovens on the property, when uncontrolled,
equal to or greater than 50 tons per calendar year, shall
ensure that
the overall emission reduction from the uncontrolled VOC emission rate of
the oven(s) will be
[
(C)
Each bakery in the Dallas/Fort Worth area with a total
weight of VOC emitted from all bakery ovens on the property, when uncontrolled,
equal to or greater than 25 tons per calendar year, but less than 50 tons
per calendar year, shall reduce total VOC emissions by at least 30% from the
bakery's 1990 [
(D)
Each bakery in the El Paso area with a total weight of
VOC emitted from all bakery ovens on the property, when uncontrolled, equal
to or greater than 25 tons per calendar year shall reduce total VOC emissions
by at least 30% from the bakery's 1990 [
(E)
(No change.)
(4)
Any vent gas stream that becomes subject to the provisions
of paragraphs (1), (2), or (3) of this subsection by exceeding provisions
of §115.127(a) of this title (relating to Exemptions) shall remain subject
to the provisions of this subsection, even if throughput or emissions later
fall below the exemption limits unless and until emissions are reduced to
no more than the controlled emissions level existing before implementation
of the project by which throughput or emission rate was reduced to less than
the applicable exemption limits in §115.127(a) of this title
;
and:
(A)
the project by which throughput or emission rate was reduced
is authorized by any permit or permit amendment or standard permit or
permit by rule
[
(B)
if authorization by permit, permit amendment, standard
permit, or
permit by rule
[
(b)
For all persons in Nueces and Victoria Counties, any vent
gas streams affected by §115.121(b) of this title must be controlled
properly with a control efficiency of at least 90% or to a VOC concentration
of no more than 20 ppmv (on a dry basis corrected to 3.0% oxygen for combustion
devices):
(1) - (2)
(No change.)
(3)
by any other vapor
control
[
(c)
For all persons in Aransas, Bexar, Calhoun, Matagorda,
San Patricio, and Travis Counties, the following control requirements shall
apply
.
[
(1)
Any vent gas streams affected by §115.121(c)(1) of
this title must be controlled properly:
(A) - (B)
(No change.)
(C)
by any other vapor
control
[
(2)
Any vent gas streams affected by §115.121(c)(2) of
this title must be controlled properly:
(A)
(No change.)
(B)
by any other vapor
control
[
(3)
Any vent gas streams affected by §115.121(c)(3) of
this title must be controlled properly:
(A)
(No change.)
(B)
by any other vapor
control
[
(4)
Any vent gas streams affected by §115.121(c)(4) of
this title must be controlled properly:
(A)
(No change.)
(B)
by any other vapor
control
[
§115.125.Testing Requirements.
[
Compliance with the emission specifications,
vapor control system efficiency, and certain control requirements and exemption
criteria of §§115.121 - 115.123 and 115.127 of this title (relating
to Emission Specifications; Control Requirements; Alternate Control Requirements;
and Exemptions)
[
(1)
Flow rate. Test Methods 1-4
(40 Code of Federal Regulations (CFR) 60, Appendix A) are used for determining
flow rates, as necessary.
(2)
Concentration of volatile organic
compounds (VOC).
(A)
Test Method 18 (40 CFR 60, Appendix A) is used
for determining gaseous organic compound emissions by gas chromatography.
(B)
Test Method 25 (40 CFR 60, Appendix A) is used
for determining total gaseous nonmethane organic emissions as carbon.
(C)
Test Methods 25A or 25B (40 CFR 60, Appendix
A) are used for determining total gaseous organic concentrations using flame
ionization or nondispersive infrared analysis.
(3)
Performance requirements for flares and
vapor combustors.
(A)
[
(B)
[
(C)
For flares in the Beaumont/Port
Arthur, Dallas/Fort Worth, and Houston/Galveston areas, the performance test
requirements of 40 CFR 60.18(b) shall apply.
(D)
For vapor combustors, the owner
or operator may consider the unit to be a flare and meet the performance test
requirements of 40 CFR 60.18(b) rather than the procedures of paragraphs (1)
and (2) of this section.
(E)
Compliance with the requirements
of 40 CFR 60.18(b) will be considered to demonstrate compliance with the emission
specifications and control efficiency requirements of §115.121 and §115.122
of this title.
[
Test Methods 1-4 (40 Code
of Federal Regulations 60, Appendix A) for determining flow rate, as necessary;]
[
Test Method 18 (40 Code of
Federal Regulations 60, Appendix A) for determining gaseous organic compound
emissions by gas chromatography;]
[
Test Method 25 (40 Code of
Federal Regulations 60, Appendix A) for determining total gaseous nonmethane
organic emissions as carbon;]
[
Test Methods 25A or 25B (40
Code of Federal Regulations 60, Appendix A) for determining total gaseous
organic concentrations using flame ionization or nondispersive infrared analysis;
or]
(4)
[
(5)
Alternate test methods. Test
methods other than those specified in paragraphs (1) - (3) of this section
may be used if validated by 40 CFR 63, Appendix A, Test Method 301 (effective
December 29, 1992). For the purposes of this paragraph, substitute "executive
director" each place that Test Method 301 references "administrator."
[
For Nueces and Victoria Counties,
compliance with §115.121(b) of this title shall be determined by applying
the following test methods, as appropriate:]
[
Test Method 22 (40 Code of Federal Regulations
60, Appendix A) for visual determination of fugitive emissions from material
sources and smoke emissions from flares;]
[
additional test method requirements for flares
described in 40 Code of Federal Regulations 60.18(f);]
[
Test Methods 1-4 (40 Code of Federal Regulations
60, Appendix A) for determining flow rate, as necessary;]
[
Test Method 18 (40 Code of Federal Regulations
60, Appendix A) for determining gaseous organic compound emissions by gas
chromatography;]
[
Test Method 25 (40 Code of Federal Regulations
60, Appendix A) for determining total gaseous nonmethane organic emissions
as carbon;]
[
Test Methods 25A or 25B (40 Code of Federal
Regulations 60, Appendix A) for determining total gaseous organic concentrations
using flame ionization or nondispersive infrared analysis; or]
[
minor modifications to these test methods approved
by the executive director.]
§115.126.Monitoring and Recordkeeping Requirements.
[
The
[
(1)
Vapor control systems. For vapor control systems used
to control emissions in Victoria County and in the Beaumont/Port Arthur, Dallas/Fort
Worth, El Paso, and Houston/Galveston areas from vents subject to
[
(A)
continuous monitoring
and recording
of
:
(i)
the exhaust gas temperature immediately downstream
of a direct-flame incinerator;
(ii)
[
(iii)
[
(iv)
the exhaust gas temperature
immediately downstream of a vapor combustor. Alternatively, the owner or operator
of a vapor combustor may consider the unit to be a flare and meet the requirements
specified in 40 Code of Federal Regulations (CFR) 60.18(b) and Chapter 111
of this title (relating to Control of Air Pollution from Visible Emissions
and Particulate Matter) for flares;
(B)
in the Beaumont/Port Arthur,
Dallas/Fort Worth, and Houston/Galveston areas, the requirements specified
in 40 CFR 60.18(b) and Chapter 111 of this title for flares; and
(C)
for vapor control systems other than those
specified in subparagraphs (A) and (B) of this paragraph, records of appropriate
operating parameters
.
(2)
[
Test results. A record
of
the results of any testing [
(3)
[
(A)
the pounds of ethylene emitted per 1,000 pounds of low-density
polyethylene produced;
(B)
the combined weight of VOC of each vent gas stream on a
daily basis;
and
(C)
the
concentration
[
[
the results of any testing
of any vent conducted at an affected facility in accordance with the provisions
specified in this section.]
(4)
[
(5)
[
(A)
The owner or operator of each
bakery in the Houston/Galveston area with a total weight of VOC emitted from
all bakery ovens on the property, when uncontrolled, equal to or greater than
25 tons per calendar year, shall submit a control plan no later than March
31, 2001, to the executive director, the appropriate regional office, and
any local air pollution control program with jurisdiction. The plan shall
demonstrate that the overall emission reduction from the uncontrolled VOC
emission rate of the oven(s) will be at least 80% by December 31, 2001. At
a minimum, the control plan shall include the emission point number (EPN)
and the facility identification number (FIN) of each bakery oven and any associated
control device, a plot plan showing the location, EPN, and FIN of each bakery
oven and any associated control device, and the 2000 VOC emission rates (consistent
with the bakery's 2000 emissions inventory). The projected 2002 VOC emission
rates shall be calculated in a manner consistent with the 2000 emissions inventory.
[
The owner or operator of each
bakery in the Dallas/Fort Worth area with a total weight of VOC emitted from
all bakery ovens on the property, when uncontrolled, equal to or greater than
50 tons per calendar year, shall submit an initial control plan no later than
March 31, 2000, to the executive director, the appropriate regional office,
and any local air pollution control program with jurisdiction which demonstrates
that the overall reduction of VOC emissions from the bakery's 1990 baseline
emissions inventory will be at least 80% by December 31, 2000. At a minimum,
the control plan shall include the emission point number (EPN) and the facility
identification number (FIN) of each bakery oven and any associated control
device, a plot plan showing the location, EPN, and FIN of each bakery oven
and any associated control device, and the 1990 VOC emission rates (consistent
with the bakery's 1990 emissions inventory). The projected 2000 VOC emission
rates shall be calculated in a manner consistent with the 1990 emissions inventory.]
[
In order to document continued
compliance with §115.122(a)(3) of this title, the owner or operator of
each bakery specified in clauses (i) and (ii) of this subparagraph shall submit
an annual report no later than March 31 of each year to the executive director,
the appropriate regional office, and any local air pollution control program
with jurisdiction which demonstrates the overall reduction of VOC emissions
from the bakery's 1990 baseline emissions inventory during the preceding calendar
year. At a minimum, the report shall include the EPN and FIN of each bakery
oven and any associated control device, a plot plan showing the location,
EPN, and FIN of each bakery oven and any associated control device, and the
VOC emission rates. The emission rates for the proceeding calendar year shall
be calculated in a manner consistent with the 1990 emissions inventory.]
[
The owner or operator of each bakery in the
Houston/Galveston area with VOC emissions, when uncontrolled, equal to or
greater than 25 tons per calendar year, shall submit an annual report which
demonstrates that the overall reduction of VOC emissions from the bakery's
1990 baseline emissions inventory during the preceding calendar year is at
least 30% after May 31, 1996.]
[
Beginning in 2002, the owner or operator of
each bakery in the Dallas/Fort Worth area with VOC emissions, when uncontrolled,
equal to or greater than 50 tons per calendar year, shall submit an annual
report which demonstrates that the overall reduction of VOC emissions from
the bakery's 1990 baseline emissions inventory during the preceding calendar
year is at least 80% after December 31, 2000.]
(B)
[
(6)
[
(A)
No later than six months after the commission publishes
notification in the
Texas Register
as specified
in
§115.129(d) or (e)
[
(B)
In order to document continued compliance with §115.122(a)(3)
of this title, the owner or operator of each bakery shall submit an annual
report no later than March 31 of each year to the executive director, the
appropriate regional office, and any local air pollution control program with
jurisdiction which demonstrates that the overall reduction of VOC emissions
from the bakery's 1990 [
(C)
All representations in [
(7)
[
[
[
Records for each vent required
to satisfy the provisions of §115.121(b) of this title shall be sufficient
to demonstrate the proper functioning of applicable control equipment to design
specifications, including:]
[
continuous monitoring of the exhaust gas temperature
immediately downstream of a direct-flame incinerator;]
[
continuous monitoring of temperatures upstream
and downstream of a catalytic incinerator or chiller;]
[
continuous monitoring of the exhaust gas VOC
concentration of any carbon adsorption system, as defined in §101.1 of
this title;]
[
the results of any testing of any vent conducted
at an affected facility in accordance with the provisions specified in §115.125(b)
of this title.]
[
Records for each vent exempted
from control requirements in accordance with §115.127(b) of this title
shall be sufficient to demonstrate compliance with applicable exemption limits,
including:]
[
the pounds of ethylene emitted per 1,000 pounds
of low-density polyethylene produced;]
[
the combined weight of VOC of each vent gas
stream on a daily basis;]
[
the true partial pressure of VOC in each vent
gas stream on a daily basis; and]
[
the results of any testing of any vent conducted
at an affected facility in accordance with the provisions specified in this
section.]
[
As an alternative to the requirements
of paragraph (2) of this subsection, records for each vent exempted from control
requirements in accordance with §115.127(b) of this title and having
a VOC emission rate or concentration less than 50% of the applicable exemption
limits at maximum actual operating conditions shall be sufficient to demonstrate
continuous compliance with the applicable exemption limit. These records shall
include complete information from either test results or appropriate calculations
which clearly documents that the emission characteristics at maximum actual
operating conditions are less than 50% of the applicable exemption limits.
This documentation shall include the operating parameter levels that occurred
during any testing, and the maximum levels feasible for the process.]
§115.127.Exemptions.
(a)
For all persons in the Beaumont/Port Arthur, Dallas/Fort
Worth, El Paso, and Houston/Galveston areas, the following exemptions apply.
(1)
(No change.)
(2)
The following vent gas streams are exempt from the requirements
of §115.121(a)(1) of this title:
(A)
(No change.)
(B)
a vent gas stream specified in §115.121(a)(1) of this
title with a concentration of VOC less than
612 parts per million by
volume (ppmv)
[
(C)
until April 15, 2001, for facilities which have been assigned
the code number 26 as described in the document Standard Industrial Classification
(SIC) Manual, 1972, as amended by the 1977 Supplement, a vent gas stream specified
in §115.121(a)(1) of this title with a concentration of VOC less than
30,000 ppmv
[
(D) - (E)
(No change.)
(3)
The following vent gas streams are exempt from the requirements
of §115.121(a)(2)(B) - (E) of this title:
(A)
(No change.)
(B)
a vent gas stream from any air oxidation synthetic organic
chemical manufacturing process with a concentration of VOC less than
612 ppmv
[
(C)
a vent gas stream from any liquid phase polypropylene manufacturing
process, any liquid phase slurry high-density polyethylene manufacturing process,
and any continuous polystyrene manufacturing process with a concentration
of VOC less than
408 ppmv
[
(4)
For synthetic organic chemical manufacturing industry (SOCMI)
reactor processes and distillation operations:
(A) - (B)
(No change.)
(C)
Any reactor process or distillation operation vent gas
stream with a flow rate less than 0.011 standard cubic meters per minute or
a VOC concentration less than 500
ppmv
[
(D) - (E)
(No change.)
(5) - (7)
(No change.)
(8)
As an alternative to complying
with the requirements of this division (relating to Vent Gas Control) (or,
in the case of bakeries, as an alternative to complying with the requirements
of §115.121(a)(1) and §115.122(a)(1) of this title) for a source
that is addressed by a Chapter 115 contingency rule (i.e., one in which Chapter
115 requirements are triggered for that source by the commission publishing
notification in the
Texas Register
that implementation
of the contingency rule is necessary), the owner or operator of that source
may instead choose to comply with the requirements of the contingency rule
as though the contingency rule already had been implemented for that source.
The owner or operator of each source choosing this option shall submit written
notification to the executive director and any local air pollution control
program with jurisdiction. When the executive director and the local program
(if any) receive such notification, the source will then be considered subject
to the contingency rule as though the contingency rule already had been implemented
for that source.
(b)
For all persons in Nueces and Victoria Counties, the following
exemptions apply.
(1)
(No change.)
(2)
The following vent gas streams are exempt from the requirements
of §115.121(b) of this title:
(A)
(No change.)
(B)
a vent gas stream with a concentration of the VOC or classes
of compounds specified in §115.121(b)(2) and (3) of this title less than
30,000 ppmv
[
(3) - (4)
(No change.)
(c)
For all persons in Aransas, Bexar, Calhoun, Matagorda,
San Patricio, and Travis Counties, the following exemptions apply.
(1)
The following vent gas streams are exempt from the requirements
of §115.121(c)(1) of this title:
(A) - (B)
(No change.)
(C)
a vent gas stream having a concentration of the VOC specified
in §115.121(c)(1)(B) and (C) of this title less than
30,000 ppmv
[
(2) - (4)
(No change.)
§115.129.Counties and Compliance Schedules.
(a)
The owner or operator of each vent gas
stream in Aransas, Bexar, Brazoria, Calhoun, Chambers, Collin, Dallas, Denton,
El Paso, Fort Bend, Galveston, Hardin, Harris, Jefferson, Liberty, Matagorda,
Montgomery, Nueces, Orange, San Patricio, Tarrant, Travis, Victoria, and Waller
Counties shall continue to comply with this division (relating to Vent Gas
Control) as required by §115.930 of this title (relating to Compliance
Dates).
[
[
All affected synthetic organic
chemical manufacturing industry reactor process or distillation operations
in Brazoria, Chambers, Collin, Dallas, Denton, El Paso, Fort Bend, Galveston,
Hardin, Harris, Jefferson, Liberty, Montgomery, Orange, Tarrant, and Waller
Counties shall be in compliance with §115.121(a)(2)(A) of this title
(relating to Emission Specifications) as soon as practicable, but no later
than November 15, 1996.]
(b)
[
(c)
[
(d)
[
(e)
[
(f)
The owner or operator of each
flare in Brazoria, Chambers, Collin, Dallas, Denton, Fort Bend, Galveston,
Hardin, Harris, Jefferson, Liberty, Montgomery, Orange, Tarrant, and Waller
Counties which is used to comply with the requirements of §115.121 and/or §115.122
of this title shall comply with §115.125(3)(C) and §115.126(1)(B)
of this title (relating to Testing Requirements; and Monitoring and Recordkeeping
Requirements) as soon as practicable, but no later than December 31, 2001.
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed
with the Office of the Secretary of State, on August 11, 2000.
TRD-200005637
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
30 TAC §§115.161, 115.162, 115.164 - 115.167, 115.169
STATUTORY AUTHORITY
The amendments are proposed under the Texas Health and Safety Code, Texas
Clean Air Act, (TCAA), §382.011, concerning General Powers and Duties,
which provides the commission with the authority to establish the level of
quality to be maintained in the state's air and the authority to control the
quality of the state's air; §382.017, concerning Rules, which provides
the commission with the authority to adopt rules consistent with the policy
and purposes of the TCAA; and §382.012, concerning State Air Control
Plan, which requires the commission to develop plans for protection of the
state's air.
The amendments implement the Texas Health and Safety Code, TCAA, §§382.011,
382.012, and 382.017.
§115.161.Applicability.
(a)
The provisions of §§115.162 - 115.167 of this
title (relating to Control Requirements; Alternate Control Requirements; Determination
of Emissions and Flow Rates; Approved Test Methods and Testing Requirements;
Monitoring and Recordkeeping Requirements; and Exemptions) apply to vent gas
streams at batch process operations in the Beaumont/Port Arthur
and Houston/Galveston
areas
[
(1) - (7)
(No change.)
(b)
(No change.)
§115.162.Control Requirements.
The owner or operator of each batch process operation in the Beaumont/Port
Arthur
and Houston/Galveston areas
[
(1) - (3)
(No change.)
§115.164.Determination of Emissions and Flow Rates.
The owner or operator of each batch process operation in the Beaumont/Port
Arthur
and Houston/Galveston areas
[
(1) - (2)
(No change.)
§115.165.Approved Test Methods and Testing Requirements.
The owner or operator of each batch process operation in the Beaumont/Port
Arthur
and Houston/Galveston areas
[
(1) - (2)
(No change.)
§115.166.Monitoring and Recordkeeping Requirements.
The owner or operator of each batch process operation in the Beaumont/Port
Arthur
and Houston/Galveston areas
[
(1)
Vapor control systems. For vapor control systems used to
control emissions from
batch process
[
(A)
continuous monitoring and recording of:
(i) - (ii)
(No change.)
(iii)
for an absorber, either:
(I)
(No change.)
(II)
the concentration level of
volatile organic compounds
(VOC)
[
(iv) - (vii)
(No change.)
(B) - (C)
(No change.)
(2) - (3)
(No change.)
§115.167.Exemptions.
The following exemptions apply [
(1)
Batch process operations at an account which has total
volatile organic compound (VOC) emissions (determined before control but
after the last recovery device) of less than
the following rates
[
(A)
100 tons per year (tpy) in
the Beaumont/Port Arthur area; and
(B)
25 tpy in the Houston/Galveston
area.
(2)
The following are exempt from the requirements of this
division, except for
§115.164 and
§115.166(2) and (3)
of this title (relating to
Determination of Emissions and Flow Rates;
and
Monitoring and Recordkeeping Requirements):
(A) - (B)
(No change.)
§115.169.Counties and Compliance Schedules.
(a)
The owner or operator of each batch process
operation in Hardin, Jefferson, and Orange Counties shall be in compliance
with this division (relating to Batch Processes) as soon as practicable, but
no later than December 31, 2001. All batch process operations subject to this
division in Hardin, Jefferson, and Orange Counties shall continue to comply
with the requirements of Division 2 of this subchapter (relating to Vent Gas
Control) until these batch process operations are in compliance with the requirements
of this division.
(b)
The owner or operator of each
batch process operation in Brazoria, Chambers, Fort Bend, Galveston, Harris,
Liberty, Montgomery, and Waller Counties shall be in compliance with this
division (relating to Batch Processes) as soon as practicable, but no later
than December 31, 2002. All batch process operations subject to this division
in Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery,
and Waller Counties shall continue to comply with the requirements of Division
2 of this subchapter (relating to Vent Gas Control) until these batch process
operations are in compliance with the requirements of this division.
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed
with the Office of the Secretary of State, on August 11, 2000.
TRD-200005636
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
1.
LOADING AND UNLOADING OF VOLATILE ORGANIC COMPOUNDS
30 TAC §§115.211, 115.212, 115.216
STATUTORY AUTHORITY
The amendments are proposed under the Texas Health and Safety Code, Texas
Clean Air Act (TCAA), §382.011, concerning General Powers and Duties,
which provides the commission with the authority to establish the level of
quality to be maintained in the state's air and the authority to control the
quality of the state's air; §382.017, concerning Rules, which provides
the commission with the authority to adopt rules consistent with the policy
and purposes of the TCAA; and §382.012, concerning State Air Control
Plan, which requires the commission to develop plans for protection of the
state's air.
The proposed amendments implement the Texas Health and Safety Code, TCAA, §§382.011,
382.012, and 382.017.
§115.211.Emission Specifications.
The owner or operator of each gasoline terminal [
(1) - (2)
(No change.)
§115.212.Control Requirements.
(a)
The owner or operator of each volatile organic compound
(VOC) transfer operation, transport vessel, and marine vessel in the Beaumont/Port
Arthur, Dallas/Fort Worth, El Paso, and Houston/Galveston areas shall comply
with the following control requirements.
(1) - (2)
(No change.)
(3)
Leak-free requirements. All land-based [
(A) - (E)
(No change.)
(4) - (7)
(No change.)
(b)
The owner or operator of each land-based VOC transfer operation
and transport vessel in the covered attainment counties shall comply with
the following control requirements.
(1) - (2)
(No change.)
(3)
Leak-free requirements. All land-based [
(A) - (E)
(No change.)
(4) - (5)
(No change.)
§115.216.Monitoring and Recordkeeping Requirements.
The owner or operator of each volatile organic compound (VOC) loading
or unloading operation in the covered attainment counties or in the Beaumont/Port
Arthur, Dallas/Fort Worth, El Paso, and Houston/Galveston areas shall maintain
the following information for at least two years at the plant, as defined
by its air quality account number. The owner or operator shall make the information
available upon request to representatives of the executive director, EPA,
or any local air pollution control agency having jurisdiction in the area.
(1) - (2)
(No change.)
(3)
Land-based VOC transfer to or from transport vessels.
(A)
A daily record of:
(i)
the identification number of each tank-truck tank
for which annual leak testing is required under §115.214(a)(1)(C) or
(b)(1)(C) of this title (relating to Inspection Requirements)
;
(ii)
(No change.)
(iii)
the date of the last leak testing of each tank-truck
tank as required by §115.214(a)(1)(C) or (b)(1)(C) of this title [
(B) - (E)
(No change.)
(4)
(No change.)
This agency hereby certifies that the proposal has been
reviewed by legal counsel and found to be within the agency's legal authority
to adopt.
Filed
with the Office of the Secretary of State, on August 11, 2000.
TRD-200005635
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
30 TAC §115.240
STATUTORY AUTHORITY
The new section is proposed under the Texas Health and Safety Code, Texas
Clean Air Act (TCAA), §382.011, concerning General Powers and Duties,
which provides the commission with the authority to establish the level of
quality to be maintained in the state's air and the authority to control the
quality of the state's air; §382.017, concerning Rules, which provides
the commission with the authority to adopt rules consistent with the policy
and purposes of the TCAA; and §382.012, concerning State Air Control
Plan, which requires the commission to develop plans for protection of the
state's air.
The proposed new section implements the Texas Health and Safety Code, TCAA, §§382.011,
382.012, and 382.017.
§115.240.Stage II Vapor Recovery Definitions.
The following words and terms, when used in this division, shall have
the following meanings, unless the context clearly indicates otherwise. Additional
definitions for terms used in this division are found in §115.10 of this
title (relating to Definitions), §101.1 of this title (relating to Definitions),
and §3.2 of this title (relating to Definitions).
(1)
Independent small business marketer of gasoline - A person
engaged in the marketing of gasoline who owns the dispensing equipment at
a motor vehicle fuel dispensing facility and receives at least 50% of his
annual income from the marketing of gasoline. A person is not an independent
small business marketer of gasoline if such person:
(A)
is a refiner; or
(B)
controls (i.e., owns more than 50% of a business or corporation's
stock), is controlled by, or is under common control with, a refiner; or
(C)
is otherwise directly or indirectly affiliated with a refiner
or with a person who controls, is controlled by, or is under common control
with a refiner (unless the sole affiliation is by means of a supply contract
or an agreement or contract to use a trademark, trade name, service mark,
or other identifying symbol or name owned by such refiner or any such person).
(2)
Owner or operator of a motor vehicle fuel dispensing facility
- Any person who owns, leases, operates, or controls the motor vehicle fuel
dispensing facility.
This agency hereby certifies that the proposal has been
reviewed by legal counsel and found to be within the agency's legal authority
to adopt.
Filed
with the Office of the Secretary of State, on August 11, 2000.
TRD-200005634
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
3.
FLEXOGRAPHIC AND ROTOGRAVURE PRINTING
30 TAC §115.430
STATUTORY AUTHORITY
The new section is proposed under the Texas Health and Safety Code, Texas
Clean Air Act (TCAA), §382.011, concerning General Powers and Duties,
which provides the commission with the authority to establish the level of
quality to be maintained in the state's air and the authority to control the
quality of the state's air; §382.017, concerning Rules, which provides
the commission with the authority to adopt rules consistent with the policy
and purposes of the TCAA; and §382.012, concerning State Air Control
Plan, which requires the commission to develop plans for protection of the
state's air.
The proposed new section implements the Texas Health and Safety Code, TCAA, §§382.011,
382.012, and 382.017.
§115.430.Flexographic and Rotogravure Printing Definitions.
The following words and terms, when used in this division, shall have
the following meanings, unless the context clearly indicates otherwise. Additional
definitions for terms used in this division are found in §115.10 of this
title (relating to Definitions), §101.1 of this title (relating to Definitions),
and §3.2 of this title (relating to Definitions).
(1)
Flexographic printing process - A method of printing in
which the image areas are raised above the non-image areas, and the image
carrier is made of an elastomeric material.
(2)
Packaging rotogravure printing - Any rotogravure printing
upon paper, paper board, metal foil, plastic film, or any other substrate
which is, in subsequent operations, formed into packaging products or labels.
(3)
Publication rotogravure printing - Any rotogravure printing
upon paper which is subsequently formed into books, magazines, catalogues,
brochures, directories, newspaper supplements, or other types of printed materials.
(4)
Rotogravure printing - The application of words, designs,
and/or pictures to any substrate by means of a roll printing technique which
involves a recessed image area. The recessed area is loaded with ink and pressed
directly to the substrate for image transfer.
This agency hereby certifies that the proposal has been
reviewed by legal counsel and found to be within the agency's legal authority
to adopt.
Filed
with the Office of the Secretary of State, on August 11, 2000.
TRD-200005633
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
30 TAC §115.449
STATUTORY AUTHORITY
The amendment is proposed under the Texas Health and Safety Code, Texas
Clean Air Act (TCAA), §382.011, concerning General Powers and Duties,
which provides the commission with the authority to establish the level of
quality to be maintained in the state's air and the authority to control the
quality of the state's air; §382.017, concerning Rules, which provides
the commission with the authority to adopt rules consistent with the policy
and purposes of the TCAA; and §382.012, concerning State Air Control
Plan, which requires the commission to develop plans for protection of the
state's air.
The proposed amendment implements the Texas Health and Safety Code, TCAA, §§382.011,
382.012, and 382.017.
§115.449.Counties and Compliance Schedules.
(a) - (c)
(No change.)
(d)
In Brazoria, Chambers, Fort
Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, all offset
lithographic printing presses on a property which, when uncontrolled, emit
a combined weight of VOC equal to or greater than 25 tons per calendar year,
shall be in compliance with §§115.442, 115.443, 115.445, and 115.446
of this title as soon as practicable, but no later than December 31, 2002.
(e)
[
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed
with the Office of the Secretary of State, on August 11, 2000.
TRD-200005632
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-0348
4.
EMISSIONS TRADING
30 TAC §115.950
The Texas Natural Resource Conservation Commission (commission)
proposes an amendment to §115.950, Emissions Trading. This amendment
is also proposed as a revision to the Texas state implementation plan (SIP).
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES
Section 115.950 currently refers to 30 TAC §101.29, Emissions Credit
Banking and Trading, as a method of meeting emission requirements of Chapter
115. In concurrent rulemaking, §101.29 would be repealed and its requirements
transferred and amended in new Chapter 101, Subchapter H, Divisions 1 and
4. This rulemaking would amend §115.950 to cite the correct cross-reference.
The amended section would require the user of credits to obtain additional
emission reduction credits or achieve lower actual emissions if new lower
volatile organic compound (VOC) emission specifications are established by
future amendments to this chapter.
The commission solicits 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.
SECTION BY SECTION DISCUSSION
Section 115.950 would be amended to change the title to "Use of Emissions
Credits for Compliance" from "Emissions Trading" to more clearly reflect the
language in §115.950, which discusses how to use emission reduction credits
for alternative compliance, not how to trade emission reduction credits.
The proposed §115.950(a) removes the reference to §101.29 and
corrects the reference to Chapter 101, Subchapter H, Division 1, Emission
Reduction Credit Banking and Trading, or Division 4, Discrete Emission Reduction
Banking and Trading. In addition, the amendment clarifies that emission reduction
credits (ERCs), mobile emission reduction credits (MERCs), discrete emission
reduction credit (DERCs), or mobile discrete emission reduction credit (MDERCs)
may be used to meet any of the requirements of Chapter 115. The term "RC"
refers to an ERC, MERC, DERC, or MDERC.
The proposed §115.950(b) adds language requiring that owners or operators
using Chapter 101, Subchapter H, Division 1 or Division 4 to meet the emission
control requirements of Chapter 115 must obtain additional RCs or reduce actual
emissions if any lower VOC emission specification is established by future
amendments to Chapter 115.
FISCAL NOTE: COST TO STATE AND LOCAL GOVERNMENT
John Davis, Technical Specialist with Strategic Planning and Appropriations,
has determined that for each year of the first five-year period the proposed
amendment is in effect, there will be no fiscal implications for any unit
of state and local government as a result of administration or enforcement
of the proposed amendment.
The proposed amendment will achieve administrative consistency with amendments
to Chapter 101 proposed in concurrent rulemaking by correcting a cross-reference,
and repealing and transferring requirements relating to Emission Credit Banking
and Trading.
The proposed amendment does not add regulatory requirements, but is being
proposed to allow compliance flexibility in meeting current or future VOC
emission limitations. The proposed amendment clarifies that ERCs, MERCs, DERCs,
or MDERCs may be used to meet any of the requirements for meeting emission
requirements. Additionally, the proposed amendment adds language to describe
how owners or operators using emission credit banking and trading to meet
the emission control requirements must obtain additional emission credits
or reduce actual emissions if any lower VOC emission specification is established
by future amendments.
PUBLIC BENEFIT AND COSTS
Mr. Davis also has determined that for each year of the first five years
the proposed amendment is in effect, the public benefit anticipated as a result
of implementing the amendment will be the increased compliance with VOC emissions
limitations through increased rule flexibility.
There are no anticipated fiscal impacts to persons and businesses as a
result of implementation of the proposed amendment, because the proposed action
is administrative in nature. The proposed amendment will correct a cross-reference
with Chapter 101, clarify the use of ERCs, MERCs, DERCs, and MERCs, and will
add language specifying that owners must obtain additional emission credits
or lower actual emissions if stricter VOC requirements are implemented through
future amendments.
SMALL AND MICRO-BUSINESS ASSESSMENT
There will be no adverse fiscal implications for small or micro-businesses
as a result of administration or enforcement of the proposed amendment. The
proposed action is administrative in nature. The proposed amendment will correct
a cross reference with Chapter 101, clarify the use of ERCs, MERCs, DERCs,
and MERCs, and will add language specifying that owners must obtain additional
emission credits or lower actual emissions if stricter VOC requirements are
implemented through future amendments to Chapter 115.
DRAFT REGULATORY IMPACT ANALYSIS
The commission has reviewed the proposed rulemaking in light of the regulatory
analysis requirements of Texas Government Code §2001.0225. The commission
has determined that the proposed amendment to Chapter 115 does not meet the
definition of a "major environmental rule" as defined in Texas Government
Code, §2001.0225. "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 commission is proposing the amendment to achieve administrative
consistency with amendments to Chapter 101 proposed in concurrent rulemaking.
The proposed amendment to Chapter 115 does not add regulatory requirements,
but is proposed to allow compliance flexibility in meeting current or future
VOC emission limitations in Chapter 115. In addition, Texas Government Code, §2001.0225,
only applies 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. This rulemaking is not subject to the regulatory analysis provisions
of §2001.0225(b), because the proposed rule does not meet any of the
four applicability requirements. Specifically, the emission banking and trading
requirements within this proposal were developed in order to meet the ozone
NAAQS set by the EPA under the Federal Clean Air Act (FCAA), §7409, and
therefore meet a federal requirement. States are primarily responsible for
ensuring attainment and maintenance of NAAQS once EPA has established those
standards. Under the FCAA, §7410 and related provisions, states must
submit, for EPA approval, SIPs that provide for the attainment and maintenance
of NAAQS through a control program directed to sources of the pollutants involved.
This proposal is not an express requirement of state law, but was developed
specifically in order to meet the air quality standards established under
federal law as NAAQS, as authorized under the TCAA, §382.012 (concerning
State Air Control Plan). This proposal is intended to help bring the HGA ozone
nonattainment area into compliance. The proposed amendments do not exceed
a standard set by federal law, exceed an express requirement of state law
unless specifically required by federal law, nor exceed a requirement of a
delegation agreement. The proposed amendments were not developed solely under
the general powers of the agency, but were specifically developed to meet
the air quality standards established under federal law as NAAQS. The commission
invites public comment on the draft regulatory impact analysis.
TAKINGS IMPACT ASSESSMENT
The commission has completed a takings impact assessment for the proposed
rule. The following is a summary of that assessment. The commission is proposing
the amendment to achieve administrative consistency with amendments to Chapter
101 proposed in concurrent rulemaking. The proposed amendment to Chapter 115
does not add regulatory requirements, but is proposed to allow compliance
flexibility in meeting current or future VOC emission limitations in Chapter
115. The proposed amendment does not affect private real 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. Consequently, the proposed
section does not meet the definition of a takings under Texas Government Code, §2007.002(5).
COASTAL MANAGEMENT PROGRAM CONSISTENCY REVIEW
The commission has determined the proposed 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'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 proposed rule is 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. The proposed amendment to Chapter 115 does not
add regulatory requirements, but is proposed to allow compliance flexibility
in meeting current or future VOC emission limitations in Chapter 115. Interested
persons may submit comments on the consistency of the proposed rule with the
CMP during the public comment period.
EFFECT ON SITES SUBJECT TO THE FEDERAL OPERATING PERMIT PROGRAM
Sources that currently have §115.590 listed in their federal operating
permit would not be required to amend the permit in response to this amendment.
However those sources that wish to use RCs to comply with this chapter must
revise their operating permit, consistent with the process in 30 TAC Chapter
122, to include the revised §115.590 requirements for each emission unit
affected by §115.590 at their site.
ANNOUNCEMENT OF HEARINGS
The commission will hold public hearings on this proposal at the following
times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention
Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m.,
Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19,
2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida
de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George
Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community
Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast
Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September
21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East
7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention
Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00
a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street,
Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic
Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central
Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite
200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource
Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin.
The hearings are structured for the receipt of oral or written comments by
interested persons. Registration will begin one hour prior to each hearing.
Individuals may present oral statements when called upon in order of registration.
A four-minute time limit will be established at each hearing to assure that
enough time is allowed for every interested person to speak. Open discussion
will not occur during each hearing; however, agency staff members will be
available to discuss the proposal one hour before each hearing, and will answer
questions before and after each hearing.
Persons with disabilities who have special communication or other accommodation
needs, who are planning to attend the hearings, should contact the Office
of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests
should be made as far in advance as possible.
SUBMITTAL OF COMMENTS
Written comments may be submitted to Heather Evans, Office of Environmental
Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087,
faxed to (512) 239-4808, or emailed to siprules@tnrcc.state.tx.us. All comments
should reference Rule Log Number 1998-089-101-AI. Comments must be received
by 5:00 p.m., September 25, 2000. For further information, please contact
Matthew R. Baker at (512) 239-1091 or Beecher Cameron at (512) 239-1495.
STATUTORY AUTHORITY
The amendment is proposed under the 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 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.
The proposed amendment implements TCAA, §382.002, relating to Policy
and Purpose; §382.011, relating to General Powers and Duties; and §382.012,
relating to State Air Control Plan.
Use of Emissions Credits for Compliance
[
An owner or operator may meet the emission
control requirements of this chapter, in whole or in part, by obtaining emission
reduction credits
(ERCs), mobile emission reduction credits (MERCs),
[
(b)
Any lower volatile organic compound (VOC)
emission specification established under this chapter for the unit or units
using RCs shall require the user of the RCs to obtain additional RCs in accordance
with Chapter 101, Subchapter H, Division 1 of this title or Chapter 101, Subchapter
H, Division 4 of this title and/or otherwise reduce emissions prior to the
effective date of such rule change. The owner or operator of the unit(s) currently
using RCs shall calculate the necessary emission reductions per unit as follows.
Figure: 30 TAC §115.950(b)
This agency hereby certifies that the proposal has been reviewed
by legal counsel and found to be within the agency's legal authority to adopt.
Filed with the Office of
the Secretary of State, on August 11, 2000.
TRD-200005657
Margaret Hoffman
Director, Environmental Law Division
Texas Natural Resource Conservation Commission
Earliest possible date of adoption: September 24, 2000
For further information, please call: (512) 239-1966
The Texas Natural Resource Conservation Commission (TNRCC or commission)
proposes amendments to §117.10, concerning Definitions; §§117.101,
117.103, 117.105, 117.106, 117.108, 117.111, 117.113, 117.116, 117.119, and
117.121, concerning Utility Electric Generation in Ozone Nonattainment Areas; §117.138,
concerning System Cap; §§117.201, 117.203, 117.205 - 117.208, 117.211,
117.213, 117.216, 117.219, and 117.221, concerning Industrial, Commercial,
and Institutional Sources in Ozone Nonattainment Areas; and §117.510
and §117.520, concerning Administrative Provisions. The commission also
proposes new §117.114 and §117.214, concerning Emission Testing
and Monitoring for the Houston/Galveston Attainment Demonstration; §117.210,
concerning System Cap; and §117.534, concerning Compliance Schedule for
Boilers, Process Heaters, and Stationary Engines at Minor Sources. The commission
also proposes new §§117.471, 117.473, 117.475, 117.478, and 117.479
in Subchapter D, to be added as a new Division 2, concerning Boilers, Process
Heaters, and Stationary Engines at Minor Sources. The proposed revisions to
Chapter 117 and to the state implementation plan (SIP) would require a wide
variety of stationary sources of nitrogen oxides (NO
x
) emissions in the Houston/Galveston (HGA) ozone nonattainment area
to meet new emission specifications and other requirements in order to reduce
NO
x
emissions and ozone air pollution.
The affected equipment types and processes include electric utility boilers
and stationary gas turbines; industrial, commercial, and institutional (ICI)
boilers and stationary gas turbines; duct burners used in turbine exhaust
ducts; process heaters and furnaces; stationary internal combustion engines;
fluid catalytic cracking units (including catalyst regenerators and associated
carbon monoxide (CO) boilers and furnaces); pulping liquor recovery furnaces,
lime kilns, lightweight aggregate kilns, heat treating furnaces, reheat furnaces,
magnesium chloride fluidized bed dryers, incinerators, and hazardous waste-fired
boilers and industrial furnaces (BIF units). The commission proposes these
amendments to Chapter 117, concerning Control of Air Pollution from Nitrogen
Compounds, and to the SIP as essential components of and consistent with the
SIP that Texas is required to develop under the Federal Clean Air Act (FCAA)
Amendments of 1990 (42 United States Code (USC)), §7410, to demonstrate
attainment of the National Ambient Air Quality Standard (NAAQS) for ozone.
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. Another purpose of these proposed revisions is to ensure that reasonably
available control technology (RACT) requirements, as required by 42 USC, §7511a(f),
are applied to major NO
x
sources in HGA which
are not subject to the previous NO
x
RACT rules.
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES
The HGA ozone nonattainment area is classified as Severe-17 under the 1990
Amendments to the FCAA (42 USC), and therefore is required to attain the one-hour
ozone standard of 0.12 parts per million (ppm) by November 15, 2007. 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 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. 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 ozone standard. 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 one-hour 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 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 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 commission 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 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.
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.
The current SIP revision contains rules, enforceable commitments, and photochemical
modeling analyses 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.
In order for the state to have an approvable attainment demonstration,
EPA has indicated that the state must adopt those strategies modeled in the
November 15, 1999 submittal and then adopt sufficient controls to close the
remaining gap in NO
x
emissions.
The Houston nonattainment area will need to ultimately reduce NO
x
more than 750 tons per day (tpd) to reach attainment with the one-hour
standard. In addition, a VOC reduction of about 25% will have to be achieved.
Adoption of point source NO
x
rules will contribute
to attainment and maintenance of the one-hour ozone standard in the HGA area.
Point source NO
x
rules also should contribute
to a successful demonstration of transportation conformity in the HGA area.
The commission solicits 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 attainment demonstration modeling produces a target emission rate of
about 66.7 tons of NO
x
per day in 2007 from industrial
point sources. The staff analyzed the most recent available point source NO
Figure 1: 30 TAC Chapter 117 - Preamble
Another table in the Tables and Graphics section of this issue of the
Figure 2: 30 TAC Chapter 117 - Preamble
The tables show that emission reductions approaching the tpd rate required
by the attainment demonstration necessitate further reductions from essentially
all categories, including electric utility boilers and stationary gas turbines;
ICI boilers and stationary gas turbines; duct burners used in turbine exhaust
ducts; process heaters and furnaces; stationary internal combustion engines;
fluid catalytic cracking units (including catalyst regenerators and CO boilers
and furnaces); pulping liquor recovery furnaces; lime kilns; lightweight aggregate
kilns; heat treating furnaces; reheat furnaces; magnesium chloride fluidized
bed dryers; incinerators; and BIF units.
To develop the information in this table and analyze the reductions obtainable
by potential NO
x
emission rate limits (in pound
per million British thermal units (lb/MMBtu) heat input, gram per horsepower-hour
(g/hp-hr), etc.), commission staff gathered the emission rate factors used
to calculate 1997 ozone season emissions for the major NO
x
sources in HGA. In January 2000, commission staff sent out a rate
data survey to major NO
x
sources in HGA and made
follow-up requests in an attempt to fill in missing rate data. In situations
where the major NO
x
sources did not or could
not provide rate data, commission staff estimated the missing rate data from
available data for similar equipment. Commission staff also conducted a quality
assurance analysis of the 1997 emissions inventory in order to correctly classify
equipment into the various categories shown in the table. The information
was compiled in a spreadsheet, allowing reductions from a rate limit applied
to an equipment category to be calculated either as a number of tons of NO
The commission staff then evaluated the emission reductions that would
be achieved by applying various attainment demonstration emission rate limits
to the equipment categories. Because some NO
x
emission sources simply can not be reasonably controlled (for example, flares),
it is necessary that the larger emission categories, especially electric utility
boilers, stationary gas turbines, heaters, engines, and ICI boilers, achieve
more than a 90% reduction in order for the overall emission reductions from
NO
x
point sources to meet the 90% goal that modeling
has shown is necessary for HGA to be able to demonstrate attainment of the
ozone NAAQS. Through an iterative process, the commission staff developed
emission rate limits for the major NO
x
point
source categories which approach the maximum practicable emission reductions
for these sources and, while technically challenging to meet, are a necessary
and essential component of the HGA Attainment Demonstration SIP, being noticed
for public hearings and comment concurrently in a separate section of this
issue of the
Texas Register
.
SECTION BY SECTION DISCUSSION
The primary purpose of the proposed revisions to Chapter 117 and to the
SIP is to establish new emission limits for the ozone attainment demonstrations.
However, another purpose of these proposed revisions is to ensure that RACT
requirements are applied to major NO
x
sources
in HGA, as required by 42 USC, §7511a(f). The current NO
x
RACT limits in §117.105, concerning Emission Specifications
for Reasonably Available Control Technology (RACT), and §117.205, concerning
Emission Specifications for Reasonably Available Control Technology (RACT),
apply to certain boilers, process heaters, and stationary internal combustion
engines and stationary gas turbines. The proposed revisions will establish
emission limits for boilers; process heaters and furnaces; stationary internal
combustion engines and stationary gas turbines; duct burners used in turbine
exhaust ducts; fluid catalytic cracking units (including catalyst regenerators
and associated CO boilers and furnaces); pulping liquor recovery furnaces;
lime kilns; lightweight aggregate kilns; heat treating furnaces; reheat furnaces;
magnesium chloride fluidized bed dryers; incinerators; and BIF units which
are currently exempt from the NO
x
RACT limits
in §117.105 and §117.205. While the proposed attainment demonstration
emission limits are more stringent than RACT, these limits will nevertheless
also fulfill the NO
x
RACT requirements of 42
USC, §7511a(f), for major sources in HGA which are not subject to the
previous NO
x
RACT rules.
The proposed changes to §117.10, concerning Definitions, revise the
definition of "low annual capacity factor boiler, process heater, or gas turbine
supplemental waste heat recovery unit" by changing the order of "commercial,
institutional, or industrial" to "industrial, commercial, or institutional"
for consistency with the title of this division. The proposed changes to §117.10
also add a definition of "electric generating facility (EGF)" which is consistent
with the corresponding definition in §117.330(12), concerning Definitions.
Subsequent definitions in §117.10 are renumbered to accommodate the proposed
new definition of "electric generating facility (EGF)."
In addition, the proposed changes to §117.10 revise the definitions
of "boiler or steam generator," "electric power generating system," "industrial
boiler or steam generator," "large DFW system," "process heater," "small DFW
system," "unit," and "utility boiler or steam generator" by deleting the superfluous
term "steam generator" since a steam generator is simply a boiler and is already
addressed by this term in the Chapter 117 rules.
The proposed changes to §117.10 also revise the definition of "unit"
to broaden its applicability. Currently, this definition includes boilers,
process heaters, stationary gas turbines, and stationary internal combustion
engines. Because the emission reductions approaching the tpd emission rate
required by the attainment demonstration necessitate further reductions from
essentially all categories, the proposed revisions broaden the applicability
of the definition of unit to include any other stationary source of NO
The proposed changes to §117.101, concerning Applicability, delete
the superfluous term "steam generator" since a steam generator is simply a
boiler and is already addressed by this term in the Chapter 117 rules, and
renumber the paragraphs accordingly. The proposed changes to §117.101
also revise a reference in the renumbered §117.101(3) from "gas turbines"
to "stationary gas turbines" for consistency with the definition of this term
in the renumbered §117.10(38), and update a reference to the renumbered §117.10(12).
The proposed changes to §117.103, concerning Exemptions, revise §117.103(a)
to specify the exemptions from the RACT requirements. The units which are
exempt from RACT are those currently exempt under this subsection from the
entire division. However, the revised language states that these units are
exempt from the specific sections for which these units would otherwise be
subject, rather than from the entire division. Although this would appear
to narrow the scope of the exemptions, it is not expected to add any additional
requirements because other sections in this division generally do not apply
to these units (except as specified in §117.113, concerning Continuous
Demonstration of Compliance). In addition, the proposed changes to §117.103
revise §117.103(a)(2) to delete the superfluous term "steam generator"
since a steam generator is simply a boiler and is already addressed by this
term in the Chapter 117 rules.
A proposed new §117.103(b) specifies that stationary gas turbines
and engines which are used solely to power other engines or gas turbines during
start-ups are exempt from the attainment demonstration requirements of §§117.106,
concerning Emission Specifications for Attainment Demonstrations; 117.108,
concerning System Cap; and 117.113, except as may be specified in §117.113(i).
The attainment demonstration exemptions do not include the RACT exemptions
for new units placed into service after November 15, 1992; utility boilers,
and auxiliary steam boilers with an annual heat input less than or equal to
2.2(10
11
) Btu per year; and stationary gas turbines
and engines which operate less than 850 hours per year, because emission reductions
from essentially all categories are necessary to approach the tpd emission
rate required by the attainment demonstration. Finally, subsections are given
titles (catchlines) to identify the topics covered.
Because the attainment demonstration exemptions do not include the RACT
exemptions for new units placed into service after November 15, 1992, the
title of Subchapter B, concerning Combustion at Existing Major Sources, is
proposed to be changed to Combustion at Major Sources.
The existing §117.103(b) includes an exemption from the oil-fired
RACT emission limits during emergency conditions which necessitate oil firing.
The proposed changes to §117.103 renumber this exemption as §117.103(c),
break it into paragraphs to make the text more readable, and revise it to
include exemption from the emission limits of §117.106, concerning Emission
Specifications for Attainment Demonstrations, and §117.108. This revision
is proposed in order to address concerns regarding times of natural gas curtailments,
which are typically a cold weather issue. Although the system cap is less
likely to be exceeded under natural gas curtailment conditions because the
30-day average winter peak electric demand is not as great as the summer 30-day
peak demand, extensive oil firing due to an emergency condition could cause
exceedances of the cap. The proposed broadening of the exemption in the renumbered §117.103(c)
will address this concern.
The proposed new §117.103(d) exempts from the requirements of Chapter
117 all combustion units which would meet the requirements of a standard permit
currently being developed for electricity-generating combustion units rated
at less than ten megawatts (MW) in capacity and which emit no more than 0.015
lb NO
x
/MMBtu heat input. The commission is proposing
this exemption to facilitate the distributed generation of electricity through
authorization of relatively small electricity-producing units.
The proposed changes to §117.105 revise §117.105(a) - (d) and
(h) to delete the superfluous term "steam generator" since a steam generator
is simply a boiler and is already addressed by this term in the Chapter 117
rules. In addition, the proposed changes to §117.105 correct the title
of §117.510 in §117.105(k)(2). The proposed changes to §117.105
also add a new §117.105(l) which specifies that after the applicable
attainment demonstration SIP compliance date(s), the RACT emission specifications
will no longer apply to equipment for which §117.106, concerning Emission
Specifications for Attainment Demonstrations, has established more stringent
emission limits. This will avoid any potential conflicts of RACT limits and
the new more stringent attainment demonstration limits.
The proposed changes to §117.106 specify new NO
x
limits for electric utility boilers located in HGA. The proposed
limits are essential components of and consistent with the HGA Attainment
Demonstration SIP, being noticed for public hearings and comment concurrently
in a separate section of this issue of the
Texas
Register
. The proposed emission limits and ozone attainment demonstration
SIP are required by 42 USC, §7410 and §7511a, which require states
to submit SIPs to the EPA which contain enforceable measures to achieve the
NAAQS. The process by which the emission limits were developed is described
in the Background and Summary of the Factual Basis for the Proposed Rules
section of this preamble.
The proposed revisions to §117.106(a) and (b) abbreviate the term
"pound per million Btu," correct a typographical error in "Beaumont/Port Arthur,"
and reorganize the syntax of these sentences for consistency with the proposed
new §117.106(c).
The proposed NO
x
emission limits for electric
utility boilers located in HGA are being added as a new §117.106(c) and
are based on a daily rate for electric utility boilers. The 24-hour emission
limit in both NO
x
RACT and these rules is designed
to limit the amount of NO
x
allowed in a 24-hour
period, in order to control peak ozone, which forms on a daily cycle. The
emission limits of §117.106(c) also apply as specified in §117.108
and in the emissions banking and trading program of Chapter 101, Subchapter
H, Division 3, concerning Mass Emissions Cap and Trade Program, being noticed
for public hearings and comment concurrently in this issue of the
Texas Register
.
The proposed limits of §117.106(c) for electric utility boilers in
HGA are part of a larger set of emission reduction measures for the HGA Attainment
Demonstration SIP. The larger context of development of the proposed NO
The proposed emission limits of 0.015 lb NO
x
/MMBtu
heat input for stationary gas turbines will achieve a 91% emission reduction
in conjunction with the proposed emission limit of 0.015 lb NO
x
per MMBtu heat input for stationary gas turbines and duct burners
in §117.206(c)(11) and (12), respectively, concerning Emission Specifications
for Attainment Demonstrations, and generate an estimated total of 141.00 tpd
NO
x
reductions from these units in HGA, based
on the 1997 emissions inventory. The proposed 91% NO
x
reduction is expected to necessitate combustion controls and flue
gas cleanup on many of the stationary gas turbines in the HGA area.
The existing §117.106(c) and (d) are proposed to be renumbered as §117.106(d)
and (e). The proposed revisions to the renumbered §117.106(d) make applicable
in HGA the ammonia and CO emission limits in order to address pollutants which
may increase as an incidental result of compliance with the proposed NO
The revisions to the renumbered §117.106(e) specify that in HGA, the
utility owner or operator may not use the trading option in §117.570.
This is necessary to ensure that any trading that occurs is done under the
emissions banking and trading program of Chapter 101, Subchapter H, Division
3, being noticed for public hearings and comment concurrently in this issue
of the
Texas Register
. The owners and operators
of the equipment addressed by these proposed Chapter 117 revisions will be
required to use the compliance flexibility provided by the proposed Chapter
101 mass emissions cap and trade program, which will allow compliance to be
established through the use of surplus reductions created from other sources.
Units which meet the definition of EGF are required to use both the system
cap specified in §117 and the mass emissions cap and trade program in
Chapter 101, Subchapter H, Division 3 to comply with the NO
x
emission specifications of §117.106(c).
Section §117.106(e) also does not allow the use of §117.107 as
an alternative for complying with the §117.106 emission specifications
for attainment demonstrations. Section 117.107 emission averaging does not
address the effects of activity level, and may not produce the intended reductions
that would be achieved with direct compliance by all units or flexible compliance
with an emission cap. Under §117.107, higher emissions will result if
units selected for less control are subsequently operated more, or if units
selected for more control are subsequently operated less. The proposed §117.106
emission limits will necessitate installation of flue gas cleanup emission
controls on a number of units. As a result, these units are likely to have
higher operating costs than units operating with only combustion controls,
creating an economic incentive to operate the best-controlled units less and
to produce greater emissions.
The proposed changes to §117.108 require the owner or operator of
each EGF in HGA to comply with the daily and 30-day system cap emission limitations
of the existing system cap. The proposed changes to §117.108 also revise §117.108(a)
- (i) and (k) by replacing references to "utility boiler" with the term "EGF."
In addition, the proposed changes to §117.108 revise §117.108(b)
by updating the reference to the definition of "electric power generating
system" in the renumbered §117.10(12).
The proposed changes to §117.108 also revise §117.108(e)(4) to
replace a reference to testing in a non-existent rule with a reference to
the maximum block one-hour emission rate as measured by the 30-day test. In
addition, the proposed changes to §117.108 revise §117.108(f) by
correcting the title in the reference to §117.119, concerning Notification,
Recordkeeping, and Reporting Requirements.
Finally, the proposed changes to §117.108 revise §117.108(i),
which specifies that an EGF which is permanently retired or decommissioned
and rendered inoperable may be included in the source cap emission limit,
to state that in HGA the permanent shutdown must have occurred after January
1, 2000. Because §117.108(c)(1) specifies 1997, 1998, and 1999 for calculating
the emissions cap, it is necessary for the shutdown to occur after this period.
Currently, EGFs in DFW may comply with §117.106 through compliance
with the daily and 30-day system cap available under §117.108. The commission
solicits comments concerning the possibility of adding flexibility for these
EGFs by allowing trading between different electric power generating systems
in DFW in order to meet the system cap of §117.108. Any such flexibility
would necessitate separate rulemaking to establish the mechanism for trading
between different electric power generating systems in DFW.
The proposed changes to §117.111, concerning Initial Demonstration
of Compliance, correct the sentence structure of §117.111(a) by changing
"be tested" to "test the units." The proposed changes to §117.111 also
correct the title of §117.510 in §117.111(a)(3), and revise §117.111(d)(3)
by replacing the term "utility boilers" with "EGFs" for consistency with the
corresponding changes to §117.108.
The proposed changes to §117.113, concerning Continuous Demonstration
of Compliance, revise a reference in §117.113(f)(2)(A)(ii) from "United
States Environmental Protection Agency" to "EPA" because this abbreviation
is defined in Chapter 3, concerning Definitions.
The proposed changes to §117.113 also revise the catchline in §117.113(g)
to clarify that these subsections apply to the NO
x
RACT emission specifications of §117.105, and revise references in §117.113(g)(1)
and (2) from "gas turbine" to "stationary gas turbine" for consistency with
the definition of this term in §117.10(37).
In addition, the proposed changes to §117.113 add a new §117.113(h)(2)
which specifies the totalizing fuel flow meter requirements for units at major
NO
x
sources in HGA which are subject to §117.106.
All units which are listed in §117.101 will be subject to the totalizing
fuel flow meter requirements because knowledge of the fuel usage is critical
in determining the emission allocations for the proposed Chapter 101 mass
emissions cap and trade program. The existing §117.113(h)(1) - (3) is
being renumbered as §117.113(h)(1)(A) - (C) to accommodate the new §117.113(h)(2).
The proposed changes to §117.113 also revise §117.113(i) to reflect
the addition of the new §117.103(b). This revision will ensure that stationary
gas turbines and engines which were required to install run time meters under
the existing RACT requirements will continue to utilize those existing run
time meters.
In addition, the proposed changes to §117.113 also revise §117.113(k)
(being renumbered as §117.113(k)(1)) to specify that this subparagraph
only applies to units in BPA or DFW, or to units in HGA which are subject
to the NO
x
RACT emission specifications of §117.105.
A new §117.113(k)(2) specifies that for units in HGA which are subject
to the attainment demonstration emission specifications of §117.106(c),
the methods required in §117.113 and §117.114 shall be used in conjunction
with the requirements of Chapter 101, Subchapter H, Division 3 to determine
compliance. The new §117.113(k)(2) further specifies that for enforcement
purposes, the executive director may also use other commission compliance
methods to determine whether the source is in compliance with applicable emission
specifications.
Finally, the proposed revisions to the catchlines in §117.113(l) clarify
that this subsection applies to the NO
x
RACT
emission specifications of §117.105.
The proposed new §117.114 applies to units in HGA which are subject
to the attainment demonstration limits of §117.106(c) and specifies monitoring
and testing requirements. The proposed new §117.114(a) requires monitoring
for NO
x
, CO, and fuel flow as specified in §117.113(a)
- (f) and (g). The proposed new §117.114(b) requires testing of each
unit which is subject to the emission limits of §117.106(c). The testing
requirements are consistent with the testing previously required of these
units for NO
x
RACT under §117.111.
Regarding emission allowances for the proposed Chapter 101 mass emissions
cap and trade program, the proposed §117.114(c) specifies that the NO
The proposed changes to §117.116, concerning Final Control Plan Procedures
for Attainment Demonstration Emission Specifications, revise the requirements
in §117.116(a)(1), (2), and (5) to apply to auxiliary boilers and stationary
gas turbines in HGA and, in conjunction with these changes, revise §117.116(a)
to refer to units listed in §117.101, rather than to utility boilers
listed in §117.101. While this change broadens the scope of the final
control plan procedures, it will not add any requirements to auxiliary boilers
and stationary gas turbines in BPA and DFW because the proposed changes to §117.116(a)(1),
(2), and (5) specify that these paragraphs only apply to utility boilers in
BPA and DFW. In addition, the remaining paragraphs in §117.116 do not
apply to auxiliary boilers and stationary gas turbines in BPA and DFW.
The proposed changes to §117.116 also revise §117.116(a)(1) to
reference the Chapter 101 mass emissions cap and trade program being proposed
concurrently in this issue of the
Texas Register
. This revision is necessary because the owners and operators of the
equipment addressed by these proposed Chapter 117 revisions will be required
to use the compliance flexibility provided by the proposed Chapter 101 mass
emissions cap and trade program, which will allow compliance to be established
through the use of surplus reductions created from other sources.
In addition, the proposed changes to §117.116 also revise §117.116(a)(3)
and (4) to add a reference to the requirements of §117.114.
The proposed changes to §117.119 revise a reference in §117.119(a)
from "Unites States Environmental Protection Agency" (which should have been
"United States Environmental Protection Agency") to "EPA" because this abbreviation
is defined in Chapter 3, concerning Definitions; and correct the reference
in §117.119(a) to §101.11 to reflect the recent title change of
this section from "Exemptions from Rules and Regulations" to "Demonstrations."
(See the July 14, 2000 issue of the
Texas Register
(25 TexReg 6727)). The proposed changes to §117.110 also revise
a reference in §117.119(d)(1)(A) from "gas turbines" to "stationary gas
turbines" for consistency with the definition of this term in §117.10(37).
The proposed changes to §117.121, concerning Alternative Case Specific
Specifications, update a reference to the existing §117.106(c) which
is being renumbered as §117.106(d) and revise a reference from "United
States Environmental Protection Agency" to "EPA" because this abbreviation
is defined in Chapter 3, concerning Definitions.
The proposed changes to §117.138, concerning System Cap, revise §117.138(b)
to update a reference to the renumbered §117.10(12).
The proposed changes to §117.201, concerning Applicability, generalize
the applicability by deleting the references to size cutoffs and adding the
following to the list of units which are subject to this division: fluid catalytic
cracking units (including CO boilers, CO furnaces, and catalyst regenerator
vents); pulping liquor recovery furnaces; lime kilns; lightweight aggregate
kilns; heat treating furnaces; reheat furnaces; magnesium chloride fluidized
bed dryers; incinerators; BIF units which were regulated as existing facilities
by the EPA at 40 Code of Federal Regulations (CFR) Part 266, Subpart H (as
was in effect on June 9, 1993); and duct burners used in turbine exhaust ducts.
It is necessary to generalize the applicability since the HGA Attainment Demonstration
SIP rules include units which are presently excluded from §117.201. These
changes do not broaden the scope of the existing rules in BPA or HGA due to
corresponding exemptions already in, or being added to, §117.203, concerning
Exemptions, and §117.205(h) which are described later in this preamble.
Finally, the proposed changes to §117.201 revise §117.201(1) by
changing the order of "commercial, institutional, or industrial" to "industrial,
commercial, or institutional" for consistency with the title of this division.
Units used to produce steam for the purpose of generating electricity, but
which are not owned or operated by a municipality or Public Utility Commission
of Texas regulated utility, are included in the applicability of §117.201,
rather than §117.101.
The proposed changes to §117.203 move the existing exemptions into
a new subsection (a) and add a new exemption for heat treating furnaces and
reheat furnaces as new §117.203(a)(3), with an expiration of this exemption
in HGA for units rated at 20 MMBtu/hr or greater after the appropriate compliance
date(s) for §117.206(c) specified in §117.520, concerning Compliance
Schedule for Commercial, Institutional, and Industrial Combustion Sources
in Ozone Nonattainment Areas. The expiration of this exemption in HGA for
certain units is necessary for consistency with the proposed §117.206(c)(14),
which establishes emission limits for these units in HGA.
In addition, the exemption in the existing §117.203(3) for electric
utility power generating boilers is proposed for deletion. Although this change
would appear to narrow the scope of the exemptions, it is not expected to
add any additional requirements to these units in BPA and DFW because other
sections in this division do not apply to these units. The requirements for
units in HGA which are not subject to §117.106 will parallel the requirements
of §117.206.
Further, the proposed changes to the renumbered §117.203(a)(4) and
(5) specify that the exemptions for incinerators, fume abaters, pulping liquor
recovery furnaces, dryers, kilns, and ovens in HGA no longer apply after the
appropriate compliance date(s) for §117.206 specified in §117.520.The
revisions to the renumbered §117.203(a)(4) and (5) are necessary for
consistency with the proposed §117.206(c)(12) - (16), which establish
emission limits for certain units in these categories in HGA.
The proposed changes to §117.203 also add a new §117.203(a)(9)
which exempts boilers and process heaters with a maximum rated capacity of
2.0 MMBtu/hr or less. This exemption level is proposed because units with
a maximum rated capacity of 2.0 MMBtu/hr or less are already regulated under
Subchapter D, Division 1, concerning Water Heaters, Small Boilers, and Process
Heaters.
In addition, the proposed changes to §117.203 add a new §117.203(b)
which specifies that the exemptions in §117.203(a)(1), (2), (6)(B), (7),
and (8)(A) no longer apply in HGA after the appropriate compliance date(s)
for emission specifications for attainment demonstrations specified in §117.520.The
expiration of these exemptions in HGA for certain units is necessary for consistency
with the proposed §117.206(c), which establishes emission limits for
these units in HGA.
The proposed new §117.203(c) exempts from the requirements of Chapter
117 all combustion units which would meet the requirements of a standard permit
currently being developed for electricity-generating combustion units rated
at less than ten MW in capacity and which emit no more than 0.015 lb NO
The proposed changes to §117.205 revise §117.205(b)(6) to include
an equation for calculating an emission limitation for each rolling 30-day
period for cases when gas fired boilers or process heaters at times also fire
gaseous fuel which contain more than 50% hydrogen by volume. The equation
uses a time weighted average to incorporate the two emission limits, from
combusting two types of gaseous fuels, into one emission limitation for each
rolling 30-day average. This proposed change is based on a rule interpretation
(Code Number R7-205.001) made by the agency's Air Rule Interpretation Team.
The proposed changes to §117.205 also revise §117.205(b)(7) by
changing references from "continuous emission monitors" to "continuous emissions
monitoring system" and from "predictive emission monitors" to "predictive
emissions monitoring system" for consistency with the definitions of these
terms in §117.10(9) and (33), respectively.
In addition, the proposed changes to §117.205 revise §117.205(c)
to allow stationary gas turbines equipped with CEMS or PEMS for CO to meet
the CO limit on a rolling 24-hour average, rather than on a one-hour average.
This revision is consistent with the corresponding CO limit for boilers and
process heaters in §117.205(f).
The proposed changes to §117.205 also revise §117.205(h)(1) by
changing the order of "commercial, institutional, or industrial" to "industrial,
commercial, or institutional" for consistency with the title of this division.
Additionally, the proposed changes to §117.205 revise the language
for fluid catalytic cracking units and duct burners in §117.205(h)(4)
and (5) for consistency with the corresponding language in §117.201(4)
and (6). The proposed changes to §117.205 also add new paragraphs (8)
- (11) for new units placed into service after November 15, 1992; ICI boilers
and process heaters with a maximum rated capacity of less than 40 MMBtu per
hour; stationary gas turbines and engines which are demonstrated to operate
less than 850 hours per year (based on a rolling 12-month average); and stationary
internal combustion engines with a horsepower (hp) rating of less than 150
hp and 300 hp in HGA and BPA, respectively.
Finally, the proposed changes to §117.205, add a new §117.205(i)
which specifies that after the applicable attainment demonstration SIP compliance
date, the RACT emission specifications will no longer apply to equipment for
which §117.206 has established a more stringent emission limit. This
will avoid any potential conflicts of RACT limits and the new more stringent
attainment demonstration limits.
The proposed changes to §117.206(a) and (b) revise references to subsections
(d) and (e), which should have been (e) and (f), to subsections (f) and (g)
to accommodate the new §117.206(c) described in the following paragraph.
In addition, the proposed changes to §117.206(b)(2) abbreviate the terms
"horsepower" and "carbon monoxide."
The proposed changes to §117.206, add a new §117.206(c) which
specifies NO
x
limits for boilers, process heaters,
stationary internal combustion engines, stationary gas turbines, fluid catalytic
cracking units (including CO boilers, CO furnaces, and catalyst regenerator
vents), BIF units, duct burners used in turbine exhaust ducts, pulping liquor
recovery furnaces, lime kilns, lightweight aggregate kilns, heat treating
furnaces, reheat furnaces, magnesium chloride fluidized bed dryers, and incinerators
at major sources of NO
x
in HGA. For units in
HGA, the emission limits in the new §117.206(c) will be used in the proposed
Chapter 101, Subchapter H, Division 3, to establish emission allocations and
shall be the lower of any applicable permit limit or the emission limits described
in the following paragraphs.
The proposed limits are essential components of and consistent with the
HGA Attainment Demonstration SIP, being noticed for public hearings and comment
concurrently in a separate section of this issue of the
Texas Register
. The proposed emission limits and ozone attainment demonstration
SIP are required by 42 USC, §7410 and §7511a, which require states
to submit SIPs to the EPA which contain enforceable measures to achieve the
NAAQS. The proposed revisions to §117.206 also update cross-references
and renumber subsequent subsections to accommodate the new emission specifications
within the section. The process by which the emission limits were developed
is described in the Background and Summary of the Factual Basis for the Proposed
Rules section of this preamble.
The proposed emission limits in §117.206(c)(1) of 0.010 lb NO
The proposed emission limit in §117.206(c)(2) of ten ppmv NO
The proposed emission limit in §117.206(c)(3) of 0.015 lb NO
The proposed emission limit in §117.206(c)(4) of 0.057 lb NO
The proposed emission limit in §117.206(c)(5) of 0.020 lb NO
The proposed emission limit in §117.206(c)(6) of 0.089 lb NO
The proposed emission limit in §117.206(c)(7) of 2.0 lb NO
x
per 1,000 gallons of oil burned for oil-fired boilers will achieve
a 90% NO
x
emission reduction and generate an
estimated 0.13 tpd NO
x
reductions in HGA, based
on the 1997 emissions inventory.
The proposed emission limits in §117.206(c)(8) of 0.010 lb NO
The proposed emission limits for stationary reciprocating internal combustion
engines in §117.206(c)(9) are: 0.17 g NO
x
/hp-hr
for gas-fired engines at sites with a total hp rating of 3,000 hp or more
in 1997 or later; 0.50 g NO
x
/hp-hr for gas-fired
engines at sites with a total hp rating of less than 3,000 hp in 1997 or later;
0.50 g NO
x
/hp-hr for existing dual-fuel, stationary
reciprocating internal combustion engines; and 0.17 g NO
x
/hp-hr for dual-fuel, stationary reciprocating internal combustion
engines initially placed into service after December 31, 2000. These emission
limits will achieve a 94% NO
x
emission reduction
and generate an estimated 78.50 tpd NO
x
reductions
in HGA, based on the 1997 emissions inventory.
The proposed emission limits for stationary gas turbines in §117.206(c)(10)
and duct burners used in turbine exhaust ducts in §117.206(c)(11) of
0.015 lb NO
x
per MMBtu heat input will achieve
a 91% NO
x
emission reduction in conjunction with
the proposed emission limit of 0.015 lb NO
x
per
MMBtu heat input for stationary gas turbines in §117.106(c)(3) and generate
an estimated total of 141.00 tpd NO
x
reductions
in HGA, based on the 1997 emissions inventory.
The proposed emission limit for pulping liquor recovery furnaces in §117.206(c)(12)
of 0.050 lb NO
x
per MMBtu heat input will achieve
a 64% NO
x
emission reduction and generate an
estimated 1.09 tpd NO
x
reductions in HGA, based
on the 1997 emissions inventory.
The proposed emission limits for kilns in §117.206(c)(13) of 0.66
lb NO
x
per ton of calcium oxide (CaO) for lime
kilns and 0.76 lb NO
x
per ton of product for
lightweight aggregate kilns will achieve a 39% NO
x
emission reduction from the kiln category and generate an estimated 0.30 tpd
NO
x
reductions in HGA, based on the 1997 emissions
inventory.
The proposed emission limits for heat treating furnaces and reheat furnaces
in §117.206(c)(14) of 0.087 lb NO
x
per MMBtu
heat input for heat treating furnaces and 0.062 lb NO
x
per MMBtu heat input for reheat furnaces will achieve a 35% NO
The proposed emission limit for magnesium chloride fluidized bed dryers
in §117.206(c)(15) of a 90% reduction from the emission factor used to
calculate the 1997 ozone season daily NO
x
emissions
will achieve a 41% NO
x
emission reduction from
the dryer category and generate an estimated 0.95 tpd NO
x
reductions in HGA, based on the 1997 emissions inventory.
The proposed emission limit for incinerators in §117.206(c)(16) of
a 90% reduction from the emission factor used to calculate the 1997 ozone
season daily NO
x
emissions will achieve a 61%
NO
x
emission reduction and generate an estimated
3.62 tpd NO
x
reductions in HGA, based on the
1997 emissions inventory.
The NO
x
emission limit averaging times for
BPA and DFW in the renumbered §117.206(d)(1) are consistent with the
averaging times for NO
x
RACT compliance, in §117.205(b)(7).
Units with NO
x
emission monitors are capable
of tracking emissions over time, and are allowed to demonstrate compliance
on a 30-day average in BPA and DFW under this subsection. The proposed changes
to §117.206 also revise §117.206(d)(1)(A) by changing references
from "continuous emission monitors" to "continuous emissions monitoring system"
and from "predictive emission monitors" to "predictive emissions monitoring
system" for consistency with the definitions of these terms in §117.10(9)
and (33), respectively. For HGA, a new §117.206(d)(2) specifies that
the averaging time for the attainment demonstration emission limits shall
be as specified in the mass emissions cap and trade program of Chapter 101,
Subchapter H, Division 3, except that EGFs shall also comply with the daily
and 30-day system cap emission limitations of §117.210, concerning System
Cap.
The emission limits of the renumbered §117.206(e) address pollutants
which may increase as an incidental result of compliance with the proposed
NO
x
limits. The CO limit is consistent with the
existing CO limit of §117.205(f) for RACT because nothing in these rules
necessitates changing the existing limit. In rulemaking adopted on April 19,
2000, the commission intended to change the proposed ammonia limit of five
ppm to ten ppm in the renumbered §117.205(e)(2) but inadvertently did
not change the rule language. (See the May 5, 2000 issue of the
Texas Register
(25 TexReg 4146).) The proposed change to the renumbered §117.206(e)(2)
makes this correction. The ammonia limit of ten ppm is lower than the existing
limit of §117.205(g) and is supported by information from SCR vendors
and ammonia test data for gas-fired boilers using SCR, not available when
the original NO
x
RACT rules were adopted in 1993.
The test data are reported in Table 2-5 of NESCAUM. It is desirable to minimize
ammonia emissions because ammonia emissions create fine particulate matter,
another form of air pollution. The commission is not including these related
pollutant limits in the attainment demonstration SIP, in order to simplify
the approval process for alternative emission specification under §107.221.
This step will eliminate the need for case-specific SIP revisions to complete
the approval of an alternate CO or ammonia limit.
With the exception of the availability of alternative CO and ammonia limits
through §117.221, the revisions to the renumbered §117.206(f) specify
that an owner or operator in HGA may not use the alternative plant-wide emission
specifications in §117.207, the alternative case-specific specifications
of §117.221, the source cap in §117.223, or the trading option in §117.570,
except that EGFs shall also comply with the daily and 30-day system cap emission
limitations of §117.210 of this title. This is necessary to ensure that
any trading that occurs is done under the Chapter 101 mass emissions cap and
trade program being noticed for public hearings and comment concurrently in
this issue of the
Texas Register
. The owners
and operators of the equipment addressed by these proposed Chapter 117 revisions
will be required to use the compliance flexibility provided by the proposed
Chapter 101 mass emissions cap and trade program, which will allow compliance
to be established through the use of surplus reductions created from other
sources.
In addition, the proposed changes to §117.206 also revise the renumbered §117.206(g)
to make the exemptions of §117.206(g)(1) and (2) unavailable in HGA for
consistency with the applicability of §117.206(c). The proposed changes
to the renumbered §117.206(g)(1) also change the order of "commercial,
institutional, or industrial" to "industrial, commercial, or institutional"
for consistency with the title of this division.
The proposed changes to §117.207, concerning Alternative Plant-wide
Emission Specifications, update cross-references to renumbered rules. The
proposed changes to §117.207 also revise §117.207(b)(1) by changing
references from "continuous emission monitors" to "continuous emissions monitoring
system" and from "predictive emission monitors" to "predictive emissions monitoring
system" for consistency with the definitions of these terms in §117.10(9)
and (33), respectively. In addition, the proposed changes to §117.207(f)
change references to §117.206(e), which should have been §117.206(f),
to §117.206(g) to account for the subsection renumbering in §117.206.
The proposed changes to §117.207 also revise references in §117.207(f)(1)
from "gas turbines" and "engines" to "stationary gas turbines" and "stationary
internal combustion engines" for consistency with the definition of these
terms in §117.10(37) and (38), respectively.
Finally, the proposed changes to §117.207(f)(4) delete the superfluous
term "steam generator" since a steam generator is simply a boiler and is already
addressed by this term in the Chapter 117 rules, and revise a reference from
"United States Environmental Protection Agency" to "EPA" because this abbreviation
is defined in Chapter 3, concerning Definitions.
The proposed changes to §117.208, concerning Operating Requirements,
correct the format of references to §§117.205 - 117.207 and 117.223
for consistency with
Texas Register
formatting
requirements, and revise a reference in §117.208(d)(4) from "gas turbines"
to "stationary gas turbines" for consistency with the definition of this term
in §117.10(37).
The proposed new §117.210 establishes a system cap for units which
generate electricity, but which will be subject to §117.206 rather than §117.106.
The proposed new §117.210, would create a flexible method of complying
with the NO
x
emission specifications proposed
in §117.206 for units which meet the definition of EGF. The proposed
section is patterned on the existing source cap compliance option in §117.108
for electric utilities. The proposed system cap sets limits on total pounds
of NO
x
allowed to be emitted by EGFs which will
not be subject to §117.106. A cap has the advantage over rate-based standards
of allowing the source owner to control the activity levels of the regulated
equipment as a means of compliance. This means that a company's compliance
measures may include installing less extensive emission controls on a piece
of equipment and choosing to operate it less, or upgrading its efficiency
to require less fuel firing.
The proposed changes to §117.211, concerning Initial Demonstration
of Compliance, revise §117.211(e)(5) by revising a reference from "United
States Environmental Protection Agency" to "EPA" because this abbreviation
is defined in Chapter 3, concerning Definitions.
The proposed changes to §117.213, concerning Continuous Demonstration
of Compliance, add a new §117.213(a)(1)(B) which specifies the totalizing
fuel flow meter requirements for units at major NO
x
sources in HGA which are subject to §117.206. All units which
are listed in §117.201 will be subject to the totalizing fuel flow meter
requirements because knowledge of the fuel usage is critical in determining
the emission allocations for the proposed Chapter 101 mass emissions cap and
trade program. The existing §117.213(a)(1)(A) - (D) is being renumbered
as §117.213(a)(1)(A)(i) - (iv) to accommodate the new §117.213(a)(1)(B).
The proposed changes to §117.213 also revise the renumbered §117.213(a)(1)(A)(ii)
(currently §117.213(a)(1)(B)) to reflect the renumbering of §117.203(6)
and (8) as §117.203(a)(6) and (8) and the addition of the new §117.205(h)(10)
- (11), and revise §117.213(b)(2)(A) and §117.213(c)(2)(A) to reflect
the addition of the new §117.205(h)(8) - (11). The existing requirement
in §117.213(b) for O
2
monitors on certain
boilers and process heaters will continue to apply to these sources in HGA
after the emission specifications of §117.206(c) supersede those of §117.205.
In addition, the proposed changes to §117.213 also add new §117.213(c)(G)
- (I) to specify that the requirement to install a CEMS or PEMS NO
x
monitor applies to the following units in HGA: lime kilns, lightweight
aggregate kilns, and units with a rated heat input greater than or equal to
100 MMBtu/hr which are subject to §117.206(c). The existing requirement
in §117.213(c) for NO
x
monitors on certain
boilers, process heaters, stationary gas turbines, and units which use a chemical
reagent for reduction of NO
x
will continue to
apply to these sources in HGA after the emission specifications of §117.206(c)
supersede those of §117.205. Similarly, the existing requirement in §117.213(d)
- (f) for CO monitoring, CEMS, and PEMS will continue to apply to these sources
in HGA after the emission specifications of §117.206(c) supersede those
of §117.205.
The proposed changes to §117.213 also revise §117.213(c)(1)(F)
and (2)(A), and (k) (being renumbered as §117.213(k)(1)) to specify
that these rules only apply to units in BPA or DFW, or to units in HGA which
are subject to the NO
x
RACT emission specifications
of §117.205. A new §117.213(k)(2) specifies that for units in HGA
which are subject to the attainment demonstration emission specifications
of §117.206(c), the methods required in §117.213 and §117.214
shall be used in conjunction with the requirements of Chapter 101, Subchapter
H, Division 3 to determine compliance. The new §117.213(k)(2) further
specifies that for enforcement purposes, the executive director may also use
other commission compliance methods to determine whether the source is in
compliance with applicable emission specifications.
In addition, the proposed changes to §117.213 revise a reference in §117.213(h)
from "gas turbines" to "stationary gas turbines" for consistency with the
definition of this term in §117.10(37); and revise §117.213(i) to
reflect the renumbering of §117.203(6)(B) as §117.203(a)(6)(B).
Finally, the proposed revisions to the catchlines in §117.213(l) and
(m) clarify that these subsections apply to the NO
x
RACT emission specifications of §117.205.
The proposed new §117.214 applies to units in HGA which are subject
to the attainment demonstration limits of §117.206(c) and specifies monitoring
and testing requirements. The proposed new §117.214(a) requires monitoring
for NO
x
, CO, and fuel flow as specified in §117.213(a)
and (c) - (f). The proposed new §117.214(b) requires testing of each
unit which is subject to the emission limits of §117.106(c). The testing
requirements are consistent with the testing previously required of these
units for NO
x
RACT under §117.211.
Regarding emission allowances for the proposed Chapter 101 mass emissions
cap and trade program, the proposed §117.214(c) specifies that the NO
The proposed changes to §117.216, concerning Final Control Plan Procedures
for Attainment Demonstration Emission Specifications, revise §117.216(a)(1)
to reference the proposed system cap of 117.210 and the Chapter 101 mass emissions
cap and trade program being proposed concurrently in this issue of the
The proposed changes to §117.219, concerning Notification, Recordkeeping,
and Reporting Requirements, amend §117.219(a) by correcting the reference
to §101.11 to reflect the recent title change of this section from "Exemptions
from Rules and Regulations" to "Demonstrations." (See the July 14, 2000 issue
of the
Texas Register
(25 TexReg 6727)).
The proposed changes to §117.219 also replace the term "performance
evaluation" with "relative accuracy test audit" in §117.219(b)(2) to
more accurately describe the CEMS or PEMS performance evaluation; and replace
the term "executive director" with "appropriate regional office" in §117.219(c)
to more precisely specify where at the agency the test results are to be sent.
In addition, the proposed changes to §117.219 revise references in §117.219(d)(1)(A)
and the renumbered §117.219(f)(4) from "gas turbine" to "stationary gas
turbine" for consistency with the definition of this term in §117.10(37).
The proposed changes to §117.219 also revise a reference in the renumbered §117.219(f)(3)
from "internal combustion engine" to "stationary internal combustion engine"
for consistency with the definition of this term in §117.10(38), and
revise a reference in the renumbered §117.219(f)(4) from "gas turbine"
to "stationary gas turbine" for consistency with the definition of this term
in §117.10(37).
In addition, the proposed revisions to §117.219(f) also renumber paragraphs
(1 ) - (8) as (2) - (9) to accommodate the new §117.219(f)(1), and add
a new §117.219(f)(1) in order to specify that records of annual fuel
usage shall be kept for each unit subject to the totalizing fuel flow meter
requirements of §117.213(a). Finally, the proposed changes to the renumbered §117.219(f)(3)(A)(i)
correct a typographical error in a reference to §117.208(d)(7).
The proposed changes to §117.221, concerning Alternative Case Specific
Specifications, revise §117.221(a) to reflect the renumbering of §117.206(d)
as §117.206(e), and revise a reference in §117.211(b) from "United
States Environmental Protection Agency" to "EPA" because this abbreviation
is defined in Chapter 3, concerning Definitions.
The proposed requirements of §117.471, concerning Applicability; §117.473,
concerning Exemptions; §117.475, concerning Emission Specifications; §117.478,
concerning Operating Requirements; and §117.479, concerning Monitoring,
Recordkeeping, and Reporting Requirements, apply to stationary reciprocating
internal combustion engines, boilers, and process heaters located in HGA at
stationary sources of NO
x
which are not major
sources of NO
x
. Therefore, a new Division 2,
concerning Boilers, Process Heaters, and Stationary Engines at Minor Sources,
is being added to Subchapter D, concerning Small Combustion Sources.
The proposed limits are essential components of and consistent with the
HGA Attainment Demonstration SIP, being noticed for public hearings and comment
concurrently in a separate section of this issue of the
Texas Register
. The proposed emission limits and ozone attainment demonstration
SIP are required by 42 USC, §7410 and §7511a, which require states
to submit SIPs to the EPA which contain enforceable measures to achieve the
NAAQS. The process by which the emission limits were developed is described
in the Background and Summary of the Factual Basis for the Proposed Rules
section of this preamble.
The proposed new §117.471 specifies that the new Division 2, concerning
Boilers, Process Heaters, and Stationary Engines at Minor Sources, which is
being added to Subchapter D, concerning Small Combustion Sources, applies
to stationary reciprocating internal combustion engines, boilers, and process
heaters located in HGA at a stationary source of NO
x
which is not a major source of NO
x
.
The proposed new §117.473 exempts boilers and process heaters with
a maximum rated capacity of 2.0 MMBtu/hr or less. This exemption level is
proposed because units with a maximum rated capacity of 2.0 MMBtu/hr or less
are already regulated under Subchapter D, Division 1, concerning Water Heaters,
Small Boilers, and Process Heaters.
In addition, the following engines are exempt in the proposed new §117.473:
engines used in research and testing; engines used for purposes of performance
verification and testing; engines used solely to power other engines or gas
turbines during start-ups; engines operated exclusively for firefighting and/or
flood control; engines used in response to and during the existence of any
officially declared disaster or state of emergency; and engines used directly
and exclusively by the owner or operator for agricultural operations necessary
for the growing of crops or raising of fowl or animals. This exemption is
consistent with the exemption in the renumbered §117.203(3) which is
available for stationary sources of NO
x
which
are major sources of NO
x
. The proposed new §117.473
also exempts stationary reciprocating internal combustion engines with a hp
rating of 50 hp or less.
In addition, the proposed new §117.473 establishes an exemption for
certain boilers and process heaters located at any stationary source of NO
The proposed new §117.473(c) exempts from the requirements of Chapter
117 all combustion units which would meet the requirements of a standard permit
currently being developed for electricity-generating combustion units rated
at less than ten MW in capacity and which emit no more than 0.015 lb NO
The proposed new §117.475 establishes a proposed emission limit of
0.036 lb NO
x
per MMBtu heat input (or alternatively,
30 ppmv NO
x
, at 3.0% O
2
, dry basis) for boilers and process heaters in HGA at non-major stationary
sources of NO
x
. The proposed new §117.475
also establishes a proposed emission limit of 0.50 g NO
x
/hp-hr for gas-fired stationary reciprocating internal combustion
engines in HGA at non-major stationary sources of NO
x
.
The proposed new §117.478 specifies techniques to be used to minimize
NO
x
emissions. The proposed §117.478(b)(1)
requires boilers to be operated with O
2
, CO,
or fuel trim. Such systems can pay for themselves with fuel savings while
reducing NO
x
due to low excess air operation
and reduced firing. Fuel trim has been demonstrated as an effective control
technique for natural gas fired boilers operating with FGR to achieve compliance
with a 30 ppmv NO
x
limit.
The proposed new §117.478(b)(2) requires operation of boilers and
process heaters equipped with forced FGR such that the proportional design
rate of FGR is maintained over the operating range.
The proposed new §117.478(b)(3) requires operation of any post combustion
controls such that the injection rate of the reducing agent (i.e., ammonia
or urea) is maintained to limit NO
x
concentrations
to no more than the NO
x
concentrations achieved
at maximum rated capacity.
The proposed new §117.478(b)(4) requires engines controlled with nonselective
catalytic reduction (NSCR) to be operated with an air-fuel ratio (AFR) controller
which operates on exhaust O
2
or CO.
The proposed new §117.478(b)(5) requires engines to be checked for
proper operation measuring and recording NO
x
and CO emissions at least quarterly and as soon as practicable after each
occurrence of engine maintenance which may reasonably be expected to increase
emissions, O
2
sensor replacement, or catalyst
cleaning or catalyst replacement. The proposed new §117.478(b)(5) allows
the use of stain tube indicators specifically designed to measure NO
The proposed new §117.479 specifies the monitoring, recordkeeping,
and reporting requirements for boilers, process heaters, and engines which
are subject to the emission specifications of §117.475.
The proposed new §117.479(a) requires installation of totalizing fuel
flow meters because knowledge of the fuel usage is critical in determining
the NO
x
emission rate as well as the emission
allocations for the proposed Chapter 101 mass emissions cap and trade program.
The proposed new §117.479(b) does not require O
2
monitors, but instead specifies that if an owner or operator installs
an O
2
monitor, then the criteria in §117.213(e)
is the appropriate guidance for the location and calibration of the monitor.
The proposed new §117.479(c) does not require NO
x
monitors, but instead specifies that if an owner or operator installs
a NO
x
monitor, then it must meet the CEMS or
PEMS requirements of §117.213(e) or (f).
The proposed new §117.479(d) specifies that monitors must be installed
on the schedule specified in §117.534.
The proposed new §117.479(e) specifies the testing requirements for
boilers, process heaters, and engines which are subject to the emission limits
of §117.475. These requirements are based upon the existing requirements
of §117.211. The proposed §117.479 also specifies that for units
without CEMS or PEMS, retesting is required after any modifications which
could increase the NO
x
emission rate, but is
optional after any modifications which could decrease the NO
x
emission rate, including, but not limited to, installation of post-combustion
controls, low-NO
x
burners, low excess air operation,
staged combustion (for example, overfire air), FGR, and fuel-lean and conventional
(fuel-rich) reburn. The NO
x
emission rate determined
by the retesting establishes a new emission factor which must be used instead
of the previously determined emission factor for the proposed Chapter 101
mass emissions cap and trade program.
The proposed new §117.479(f) specifies that the NO
x
testing and monitoring data specified in §117.479(a) - (e),
together with the level of activity, as defined in §101.350, are used
to establish the emission factor for the proposed Chapter 101 mass emissions
cap and trade program.
The proposed new §117.479(g) specifies the records to be used to demonstrate
compliance with the emission limits of §117.475.
The proposed changes to §117.510, concerning Compliance Schedule for
Utility Electric Generation, revise §117.510(c) to create separate paragraphs
in this subsection addressing compliance schedules for the NO
x
RACT rules and the proposed emission specifications for attainment
demonstrations. The commission is proposing a staged four-year implementation
schedule for compliance with the new HGA emission specifications. First, one-third
of the total reductions required to comply with the attainment demonstration
emission specifications is required by December 31, 2002. The second one-third
of the reductions is required by December 31, 2003. The final one-third of
the reductions is required by December 31, 2004. A combination of combustion
controls and flue gas cleanup controls will be necessary on many units.
The proposed revisions to §117.510(b)(2) modify the compliance schedule
for utility boilers in DFW by allowing exclusion of boilers which are to be
retired and decommissioned before May 1, 2005 from the calculation of the
emission reductions to be made by May 1, 2003. This two-year compliance schedule
extension will avoid the costs associated with installation of controls which
would be used for a relatively short period of time, yet still achieve the
necessary emission reductions before the critical 2005 ozone season. To qualify
for this compliance date extension, a boiler must be designated by the Public
Utility Commission of Texas to be necessary to operate for reliability of
the electric system, and the owner must provide the executive director an
enforceable written commitment by May 1, 2003 to retire and permanently decommission
the boiler by May 1, 2005.
In addition, the proposed changes to §117.510 add the missing word
"in" to §117.510(a)(2)(E)(iii) and (F) and the renumbered §117.510(b)(2)(A)(v)(III)
and (vi). The proposed changes to §117.510 also make a variety of minor
punctuation corrections throughout the section. Finally, the proposed changes
to §117.510 revise §117.510(a)(2)(A)(i) and the renumbered §117.510(b)(2)(A)(i)(I)
by replacing a reference to the effective date of these rules with the actual
effective date, May 11, 2000.
The proposed changes to §117.520, concerning Compliance Schedule for
Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment
Areas, revise §117.520(c) to create separate paragraphs in this subsection
addressing compliance schedules for the NO
x
RACT
rules and the proposed emission specifications for attainment demonstrations.
The commission is proposing a staged four-year implementation schedule for
compliance with the new HGA emission specifications. First, one-third of the
total reductions required to comply with the attainment demonstration emission
specifications is required by December 31, 2002. The second one-third of the
reductions is required by December 31, 2003. The final one-third of the reductions
is required by December 31, 2004. A combination of combustion controls and
flue gas cleanup controls will be necessary on many units.
In addition, the proposed changes to §117.520 add the missing word
"in" to §117.520(a)(3)(B)(v) and (E)(iii) and the renumbered §117.510(b)(2)(A)(v)(III)
and (vi). The proposed changes to §117.520 also revise §117.520(a),
(b), and (c) by changing the order of "commercial, institutional, or industrial"
to "industrial, commercial, or institutional" for consistency with the title
of this division. Finally, the proposed changes to §117.520 revise §117.520(a)(3)(A)(i)
by replacing a reference to the effective date of this rule with the actual
effective date, May 11, 2000.
The proposed new §117.534 specifies the compliance schedule for boilers,
process heaters, and stationary engines at minor sources in HGA.
PUBLIC UTILITY REGULATORY ACT DETERMINATION
As described earlier in this preamble, the commission proposes these revisions
to Chapter 117 and the SIP in order to reduce NO
x
emissions and demonstrate attainment in the HGA ozone nonattainment area.
Accordingly, the commission makes the following determination, as required
by the Public Utility Regulatory Act (PURA), Texas Utilities Code (TUC), §39.263(c)(1)(A)
and §39.263(c)(3): reductions of NO
x
made
in compliance with this rulemaking are hereby determined to be an essential
component in achieving compliance with the NAAQS for ground-level ozone; and
the amount and location of reductions of NO
x
emissions resulting from this rulemaking are hereby determined to be consistent
with the air quality goals and policies of the commission.
EFFECT ON SITES SUBJECT TO THE FEDERAL OPERATING PERMIT PROGRAM
Since Chapter 117 is an applicable requirement under 30 TAC Chapter 122,
owners or operators subject to the Federal Operating Permit Program must,
consistent with the revision process in Chapter 122, revise their operating
permit to include the revised Chapter 117 requirements for each emission unit
affected by the revisions to Chapter 117 at their site.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENTS
John Davis, Technical Specialist in the Strategic Planning and Appropriations
Section, has determined that for the first five-year period the proposed amendments
are in effect, there will be no significant fiscal implications for most units
of state government and most units of local government as a result of administration
or enforcement of the proposed amendments. However, there will be significant
fiscal implications to the University of Houston and Baylor College of Medicine
because they will be required to install emission controls on stationary sources
of NO
x
emissions as a result of the proposed
rules.
The proposed amendments would require a wide variety of stationary sources
of NO
x
emissions in HGA to meet new emission
specifications and other requirements in order to reduce NO
x
emissions and ozone air pollution. The affected equipment types and
processes include electric utility boilers and stationary gas turbines; ICI
boilers; duct burners used in turbine exhaust ducts; process heaters and furnaces;
stationary internal combustion engines; fluid catalytic cracking units (including
catalyst regenerators and associated CO boilers and furnaces); pulping liquor
recovery furnaces; lime kilns; lightweight aggregate kilns; heat treating
and reheat furnaces; magnesium chloride fluidized bed dryers; incinerators;
and BIF units.
These standards and specifications are part of the strategy to reduce emissions
of NO
x
necessary for the counties in the HGA
ozone nonattainment area to be able to demonstrate attainment with the NAAQS
for ozone. The proposed amendments are a necessary and essential component
of the proposed HGA Attainment Demonstration SIP. A SIP is a plan developed
for any region where existing (measured and estimated) ambient levels of pollutant
exceeds the levels specified in a national standard. The plan sets forth a
control strategy that provides emission reductions necessary for attainment
and maintenance of the national standards.
For sources with a design capacity to emit NO
x
in amounts greater than or equal to ten tons per year (tpy), the commission
is proposing a staged four-year implementation schedule for compliance with
the new HGA emission specifications. First, one-third of the total reductions
required to comply with the attainment demonstration emission specifications
are required by December 31, 2002. The second one-third of the reductions
are required by December 31, 2003. The final one-third of the reductions are
required by December 31, 2004. For sources with a design capacity to emit
NO
x
in amounts less than ten tpy, the final compliance
date is December 31, 2002.
Most of the sources which will have to comply with the proposed rules are
currently subject to air permits and are already being inspected for compliance.
Consequently, only a limited number of additional facilities will need to
be inspected for compliance with the proposed amendments. The commission anticipates
that enforcement of these rules will not significantly increase the number
of facilities currently inspected by the state and local governments.
The commission estimates that there may be other state and local government
facilities affected by the proposed amendments that have not been identified
in this fiscal note. State and local government facilities with equipment
affected by the proposed amendments would be required to adhere to the proposed
standards. Costs to those units would be similar as presented in this fiscal
note.
Based upon an analysis of the 1997 emission inventory database, it is anticipated
that four ICI boilers at the Baylor College of Medicine and three ICI boilers
at the University of Houston and will be affected by the proposed amendments.
The ICI boilers at the Baylor College of Medicine have a maximum capacity
less than 40 MMBtu/hr. The new NO
x
emission standard
for this type of boiler is 0.036 lb/MMBtu. It is estimated that the these
boilers will have to reduce emissions by 0.01 tpd through the use of combustion
modifications, such as low-NO
x
burners (LNB)
or FGR. Total capital costs for the combustion modifications are estimated
at $3,100 per MMBtu/hr, and the annual costs are estimated at $600 per MMBtu/hr.
These cost estimates were derived from cost models on page E-23 of EPA's alternative
control techniques (ACT) document,
Alternative Control
Techniques Document -- NO
x
Emissions from Industrial/Commercial/Institutional
(ICI) Boilers
. Total capital costs for the Baylor College of Medicine
ICI gas-fired boilers are approximately $257,000 with an annual cost of $52,200.
The average capital cost for each affected boiler is approximately $65,000
with an average annual cost of $13,000. Cost effectiveness for the proposed
emission reductions is approximately $15,000 per ton of NO
x
reduced.
The three ICI boilers at the University of Houston are larger units, with
capacities greater than 40 MMBtu/hr but less than 100 MMBtu/hr. The new NO
PUBLIC BENEFIT AND COSTS
Mr. Davis has also determined that for each year of the first five years
the proposed amendments to Chapter 117 are in effect, the public benefit anticipated
from enforcement of and compliance with the proposed amendments will be a
reduction of public exposure to NO
x
emitted from
affected stationary sources, a reduction of ground-level ozone in ozone nonattainment
areas, and conformance with the requirements of the FCAA, 42 USC, §§7410,
7502(a)(2), and 7511a(d) and (f).
The proposed amendments would require a wide variety of stationary sources
of NO
x
emissions in HGA to meet new emission
specifications and other requirements in order to reduce NO
x
emissions and ozone air pollution. The affected equipment types and
processes include electric utility boilers and stationary gas turbines; ICI
boilers; duct burners used in turbine exhaust ducts; process heaters and furnaces;
stationary internal combustion engines; fluid catalytic cracking units (including
catalyst regenerators and associated CO boilers and furnaces); pulping liquor
recovery furnaces; lime kilns; lightweight aggregate kilns; heat treating
furnaces; reheat furnaces; magnesium chloride fluidized bed dryers; incinerators;
and BIF units.
The proposed amendments do not specify a particular control technology
to achieve the emission limits and there are a variety of control technologies
or combinations of control technologies which may be used to comply, depending
on the specific circumstances of each affected source. In addition, the Chapter
101 mass emissions cap and trade program being proposed concurrently in this
issue of the
Texas Register
establishes compliance
flexibility through a mass emissions cap and trade program, which allows compliance
to be established through the use of surplus reductions created from other
sources.
There may be individual sources for which the equipment actual control
costs are higher than those identified in this cost note. The numbers of sources
affected by these rules are approximations which do not include all new sources
which have been placed into service after 1997. Because these new sources
have been permitted under rules which require the new emissions to be offset
from existing sources, the counted number of sources will not vary significantly
because of offsetting source shutdowns from obsolete equipment. The commission
anticipates costs for units not addressed in this fiscal note would be similar
to the overall findings of this analysis. Additionally, the commission has
included cost for units affected by the proposed amendments that did not report
any emission rate data for 1997. No rate data could indicate the unit has
been shut down; however, for the purpose of this note, costs were estimated
for these units and included in the overall total.
The proposed emission limit for electric utility boilers is 0.010 lb NO
Based upon an analysis of the 1997 emission inventory database, it is anticipated
that 25 utility boilers and seven auxiliary boilers in HGA will be affected
by the proposed amendments. It is estimated that these boilers will be required
to reduce NO
x
emissions by 184.26 tpd (67,255
tpy). Capital cost of the utility boiler combustion modifications is estimated
at $10/kW for the gas-fired combustion modifications, and $5/kW for the coal-fired
modifications. The costs of SCR for the coal and gas-fired utility boilers
are estimated from the cost models contained in Appendix D of
Status Report on NO
x
Control Technologies and
Cost Effectiveness for Utility Boilers
, issued by NESCAUM (June 1998).
In addition, the catalyst cost for the coal fired boilers was estimated from
discussions with engineers familiar with SCR application, and the catalyst
cost for gas-fired boilers was estimated based on more specific cost information
from gas-fired installation in the Los Angeles area, as identified in the
May 5, 2000 issue of the
Texas Register
(25
TexReg 4157). It is estimated that the cost of NO
x
reduction for the electric utility power boilers will range between approximately
$1,000 to $8,000 per ton of NO
x
reduced. There
are two utility systems affected by the proposed amendments. Total capital
cost for the first utility system with 10,069 MW of electric generating capacity
is $528 million with an increased annual cost of $88 million. This utility
system has a mixture of gas- and coal-fired boilers. The average capital cost
to gas-fired boilers in this utility system is $16 million with an average
increased annual cost of $2.6 million. The average capital cost for coal-fired
boilers in this system is $54 million with an average increased annual cost
of $9.2 million. Total capital costs for the second utility system with 532
MW of capacity are $24 million with an increased annual cost of $5 million.
The average capital cost for boilers in the smaller utility system is $12
million with an average increased annual cost of $2.3 million.
The proposed emission limits for gas-fired ICI boilers are 0.010 lb NO
Based upon an analysis of the 1997 emission inventory database, it is anticipated
that 235 gas- fired ICI boilers with a maximum rated capacity less 40 MMBtu/hr
in HGA will be affected by the proposed amendments. The commission estimates
that these boilers will be required to reduce NO
x
emissions by 0.99 tpd (361 tpy) through the use of combustion modifications.
Total capital costs for the combustion modifications are estimated at $3,100
per MMBtu/hr and the annual costs are estimated at $600 per MMBtu/hr. These
cost estimates were derived from cost models on page E-23 of EPA's
Alternative Control Techniques Document -- NO
x
Emissions from Industrial/Commercial/Institutional (ICI) Boilers
. Total
capital costs for ICI gas- fired boilers rated at 40 MMBtu/hr or less in HGA
are approximately $8.1 million with an increased annual cost of $1.6 million.
The average capital costs for boilers in this category are approximately $41,000
with an average increased annual cost of $8,300. Cost effectiveness for the
proposed emission reductions from the affected boilers in this category is
approximately $4,500 per ton of NO
x
reduced.
Based upon an analysis of the 1997 emission inventory database, it is anticipated
that 90 gas-fired ICI boilers with a maximum rated capacity equal to or greater
than 40 MMBtu/hr, but less than 100 MMBtu/hr in HGA will be affected by the
proposed amendments. The commission estimates that these boilers will be required
to reduce NO
x
emissions by 3.03 tpd (1,106 tpy)
through the use of SCR. The costs of SCR for these ICI boilers were estimated
from a spreadsheet provided by NESCAUM. Capital costs for SCR on the affected
boilers range from $68/kW to $80/kW. Total capital costs for ICI boilers with
a maximum rated capacity equal to or greater than 40 MMBtu/hr, but less than
100 MMBtu/hr in HGA are approximately $38 million with an increased annual
cost of approximately $11 million. The average capital costs for boilers in
this category are approximately $467,000 with an average increased annual
cost of $135,000. Cost effectiveness for the proposed emission reductions
from the affected boilers in this category is approximately $10,000 per ton
of NO
x
reduced.
Based upon an analysis of the 1997 emission inventory database, it is anticipated
that 180 gas- fired ICI boilers with a maximum rated capacity equal to or
greater than 100 MMBtu/hr in HGA will be affected by the proposed amendments.
The commission estimates that these boilers will be required to reduce NO
The proposed emission limit for coke-fired boilers is 0.057 lb NO
The proposed emission limit for wood fuel-fired boilers is 0.020 lb NO
The proposed emission limit for rice hull-fired boilers is 0.089 lb NO
The proposed emission limit for oil-fired boilers is 2.0 lb NO
x
per 1,000 gallons of oil burned. The proposed 90% emission reduction
is expected to necessitate SCR on the affected oil-fired boilers. Based upon
an analysis of the 1997 emission inventory database, it is anticipated that
three oil-fired ICI boilers will be affected by the proposed amendments. The
commission estimates that these boilers will be required to reduce NO
The commission estimates the total capital costs for the 513 identified
ICI boilers affected by the proposed amendments are approximately $419 million
with an annualized cost of $95 million. The overall estimated cost effectiveness
for the proposed emission reductions for ICI boilers is approximately $3,800
per ton of NO
Subchapter H. EMISSIONS BANKING AND TRADING
3.
MASS EMISSIONS CAP AND TRADE PROGRAM
4.
DISCRETE EMISSION CREDIT BANKING AND TRADING
Chapter 110.
REDUCTION OF AIR POLLUTION FROM OZONE
Chapter 114.
CONTROL OF AIR POLLUTION FROM MOTOR VEHICLES
by the commission
]
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
.
[
:
]
Imported
] - The process
by which motor
vehicle
fuel is transported into
the State
of Texas
[
counties listed in §114.319 of this title (relating
to Affected Counties and Compliance Dates)
] via
pipeline,
tank ship, rail car, tank truck, or trailer.
the
] retail
fuel dispensing facility [
, at which the fuel will be dispensed into
motor vehicles
].
transports, stores, or causes the transportation or storage of
motor vehicle fuel, produced by another person, at any point between any producer's
facility and any retail fuel dispensing outlet or bulk purchaser/consumer's
facility
].
(14)
] Motor vehicle fuel - Any
gasoline or diesel fuel used to power gasoline fueled spark-ignition or diesel
fueled compression-ignition engines.
(15)
] 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 refiner who agrees
in writing to further process the motor vehicle fuel at the refiner's refinery
and to be treated as a producer of the motor vehicle fuel, only the refiner
shall be deemed for all purposes under Subchapter H of this chapter to be
the producer of the motor vehicle fuel.
(16)
] Producer - Any person who
owns, leases, operates, controls, or supervises a production facility and/or
produces motor vehicle fuel.
(17)
] Production facility - A
facility at which motor vehicle fuel is produced.
(18)
] Refiner - Any person who
owns, leases, operates, controls, or supervises a refinery.
(19)
] Refinery - A facility that
manufactures liquid fuels by distilling petroleum.
(20)
] 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.
(21)
] Supply - To provide or transfer
fuel to a physically separate facility, vehicle, or transportation system.
Subchapter H. LOW EMISSION FUELS
The maximum sulfur content
of LED is 500 parts per million by weight per gallon.
]
programs with supporting data
], 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 subsection
(a) 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 [
in-use
] 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) of this title
[
approved by the executive director
]. 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.
to
] counties listed in §114.319 of this title (relating to Affected
Counties and Compliance Dates) shall register with the executive director
by December 1, 2001; or after May 31, 2002, within 30 days after the first
date that such person will produce or import LED. Registration shall be on
forms prescribed by the executive director and shall include a statement of
acceptance of the standards and enforcement provisions of this
division
[
chapter
]; and shall include a statement of consent by the
registrant that the executive director shall be permitted to collect samples
and access documentation and records. The executive director shall maintain
a listing of all registered suppliers.
have
] jurisdiction in the area. The product transfer documents must
contain, at a minimum, the following information:
and
]
the affected counties.
]
the following
] counties
of Texas
shall be
in compliance with §§114.312 - 114.317 of this title (relating
to Low Emission Diesel Standards; Designated
Alternate
[
Alternative
] 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
[
: Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall,
and Tarrant
].
Chapter 114.
CONTROL OF AIR POLLUTION FROM MOTOR VEHICLES
Harris County of
] the Houston/Galveston (HGA) program
area.
or Harris County
] 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.
March 15
], 2000, or in "Specifications
for Acceleration Simulation Mode (ASM-2) Vehicle Exhaust Gas Analyzer Systems
for use in the Texas Vehicle Emissions Testing Program," dated
November
1
[
March 15
], 2000. Copies of these documents are available
at the commission's Central Office, located at 12100 Park 35 Circle, Austin,
Texas 78753. The manufacturer shall also provide sufficient documentation
to demonstrate conformance with these criteria including a complete description
of all hardware components, the results of appropriate performance testing,
and a point-by-point response to each specific requirement.
acceleration simulation mode
] test and OBD test in accordance with §114.50(a)(3)
and (4)(E)
and (F)
of this title shall collect a fee of $22.50 and shall remit
$2.00 to the DPS.
Subchapter H. LOW EMISSION FUELS
4.
DIESEL EMULSION FUEL
Subchapter I. NON-ROAD ENGINES
counties listed in §114.429 of this title (relating to Affected Counties
and Compliance Schedules)
] shall not exceed the requirements of Title
13, California Code of Regulations, Chapter 9 (13 CCR 9), §2433(b), concerning
Exhaust Emission Standards and Test Procedures -- Off-Road Large Spark-Ignition
Engines, as effective on November 18, 1999.
counties listed in §114.429 of this title
] shall
not exceed the requirements of 13 CCR 9, §2433(b).
(a)
(b)
] Beginning with model year
2004
,
but no later than January 1, 2004
,
all sales of
new non-road, large spark-ignition (LSI) engines in the
State of Texas
[
affected counties
] shall comply with §114.421(b) of
this title (relating to Emissions Specifications) and §114.422 of this
title (relating to Control Requirements).
(c)
] Beginning January 1, 2004,
new non-road, LSI engines as defined in §114.420 of this title (relating
to Definitions) which are used in the
State of Texas
[
affected
counties
] shall comply with §114.421(c) of this title.
5.
NITROGEN OXIDES REDUCTION SYSTEMS
6.
LAWN SERVICE EQUIPMENT OPERATING RESTRICTIONS
7.
HOUSTON/GALVESTON AIRPORT GROUND SUPPORT EQUIPMENT
8.
HOUSTON/GALVESTON HEAVY EQUIPMENT FLEETS--COMPRESSION--IGNITION ENGINES
9.
HOUSTON/GALVESTON CONSTRUCTION EQUIPMENT OPERATING RESTRICTIONS
Subchapter J. OPERATIONAL CONTROLS FOR MOTOR VEHICLES
Chapter 115.
CONTROL OF AIR POLLUTION FROM VOLATILE ORGANIC COMPOUNDS
(1)
(2)
] Beaumont/Port Arthur area
- Hardin, Jefferson, and Orange Counties.
(3)
] Capture efficiency - The amount
of volatile organic compounds (VOC) collected by a capture system which is
expressed as a percentage derived from the weight per unit time of VOC entering
a capture system and delivered to a control device divided by the weight per
unit time of total VOC generated by a source of VOC.
(4)
] Carbon adsorption system -
A carbon adsorber with an inlet and outlet for exhaust gases and a system
to regenerate the saturated adsorbent.
(5)
] Component - A piece of equipment,
including, but not limited to pumps, valves, compressors, and pressure relief
valves, which has the potential to leak VOC.
(6)
] Continuous monitoring - Any
monitoring device used to comply with a continuous monitoring requirement
of this chapter will be considered continuous if it can be demonstrated that
at least 95% of the required data is captured.
(7)
] Covered attainment counties
- 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.
(8)
] Dallas/Fort Worth area - Collin,
Dallas, Denton, and Tarrant Counties.
(9)
] El Paso area - El Paso County.
(10)
] External floating roof -
A cover or roof in an open-top tank which rests upon or is floated upon the
liquid being contained and is equipped with a single or double seal to close
the space between the roof edge and tank shell. A double seal consists of
two complete and separate closure seals, one above the other, containing an
enclosed space between them.
For the purposes of this chapter (relating
to Control of Air Pollution from Volatile Organic Compounds), an
[
An
] external floating roof storage tank which is equipped with a self-supporting
fixed roof (typically a bolted aluminum geodesic dome) shall be considered
to be an internal floating roof storage tank.
(11)
(12)
(13)
] Fugitive emission - Any
VOC entering the atmosphere which could not reasonably pass through a stack,
chimney, vent, or other functionally equivalent opening designed to direct
or control its flow.
(14)
] Gasoline bulk plant - A
gasoline loading and/or unloading facility, excluding marine terminals, having
a gasoline throughput less than 20,000 gallons (75,708 liters) per day, averaged
over each consecutive 30-day period. A motor vehicle fuel dispensing facility
is not a gasoline bulk plant.
(15)
] Gasoline terminal - A gasoline
loading and/or unloading facility, excluding marine terminals, having a gasoline
throughput equal to or greater than 20,000 gallons (75,708 liters) per day,
averaged over each consecutive 30-day period.
(16)
] Houston/Galveston area -
Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and
Waller Counties.
(17)
(A)
(B)
(C)
(18)
] Internal floating cover
- A cover or floating roof in a fixed roof tank which rests upon or is floated
upon the liquid being contained, and is equipped with a closure seal or seals
to close the space between the cover edge and tank shell.
For the purposes
of this chapter (relating to Control of Air Pollution from Volatile Organic
Compounds), an
[
An
] external floating roof storage tank which
is equipped with a self-supporting fixed roof (typically a bolted aluminum
geodesic dome) shall be considered to be an internal floating roof storage
tank.
(19)
] Leak-free marine vessel
- A marine vessel whose cargo tank closures (hatch covers, expansion domes,
ullage openings, butterworth covers
,
and gauging covers) were inspected
prior to cargo transfer operations and all such closures were properly secured
such that no leaks of liquid or vapors can be detected by sight, sound, or
smell. Cargo tank closures shall meet the applicable rules or regulations
of the marine vessel's classification society or flag state. Cargo tank pressure/vacuum
valves shall be operating within the range specified by the marine vessel's
classification society or flag state and seated when tank pressure is less
than 80% of set point pressure such that no vapor leaks can be detected by
sight, sound, or smell. As an alternative, a marine vessel operated at negative
pressure is assumed to be leak-free for the purpose of this standard.
(20)
] Marine loading facility
- The loading arm(s), pumps, meters, shutoff valves, relief valves, and other
piping and valves that are part of a single system used to fill a marine vessel
at a single geographic site. Loading equipment that is physically separate
(i.e., does not share common piping, valves, and other loading equipment)
is considered to be a separate marine loading facility.
(21)
] Marine loading operation
- The transfer of oil, gasoline, or other volatile organic liquids at any
affected marine terminal, beginning with the connections made to a marine
vessel and ending with the disconnection from the marine vessel.
(22)
] Marine terminal - Any marine
facility or structure constructed to load oil, gasoline, or other volatile
organic liquid bulk cargo into a marine vessel. A marine terminal consists
of one or more marine loading facilities.
(23)
] Natural gas/gasoline processing
- A process that extracts condensate from gases obtained from natural gas
production and/or fractionates natural gas liquids into component products,
such as ethane, propane, butane, and natural gasoline. The following facilities
shall be included in this definition if, and only if, located on the same
property as a natural gas/gasoline processing operation previously defined:
compressor stations, dehydration units, sweetening units, field treatment,
underground storage, liquified natural gas units, and field gas gathering
systems.
(24)
(25)
(26)
] Petroleum refinery - Any
facility engaged in producing gasoline, kerosene, distillate fuel oils, residual
fuel oils, lubricants, or other products through distillation of crude oil,
or through the redistillation, cracking, extraction, reforming, or other processing
of unfinished petroleum derivatives.
(27)
] Polymer
or
[
and
] resin manufacturing process - A process that produces any of the
following polymers or resins: polyethylene, polypropylene, polystyrene, and
styrenebutadiene latex.
(28)
] Printing line - An operation
consisting of a series of one or more printing processes and including associated
drying areas.
(29)
(30)
(31)
(32)
(33)
(34)
(35)
(36)
] Synthetic organic chemical
manufacturing process - A process that produces, as intermediates or final
products, one or more of the chemicals listed in
40 Code of Federal Regulations
60.489 (effective October 18, 1983)
[
Table I of this section
].
(37)
] Tank-truck tank - Any storage
tank having a capacity greater than 1,000 gallons, mounted on a tank-truck
or trailer. Vacuum trucks used exclusively for maintenance and spill response
are not considered to be tank-truck tanks.
(38)
] Transport vessel - Any land-based
mode of transportation (truck or rail) that is equipped with a storage tank
having a capacity greater than 1,000 gallons which is used [
primarily
] to transport oil, gasoline, or other volatile organic liquid bulk
cargo. Vacuum trucks used exclusively for maintenance and spill response are
not considered to be transport vessels.
(39)
] True partial pressure -
The absolute aggregate partial pressure (psia) of all VOC in a gas stream.
(40)
] Vapor balance system - A
system which provides for containment of hydrocarbon vapors by returning displaced
vapors from the receiving vessel back to the originating vessel.
(41)
(42)
] Vapor control system
or vapor recovery system
- Any control system which utilizes vapor collection
equipment to route VOC to a control device that reduces VOC emissions.
(43)
(44)
] Vapor-tight - Not capable
of allowing the passage of gases at the pressures encountered except where
other acceptable leak-tight conditions are prescribed in
this chapter
[
the Regulations
].
(45)
] Waxy, high pour point crude
oil - A crude oil with a pour point of 50 degrees Fahrenheit (10 degrees Celsius)
or higher as determined by the American Society for Testing and Materials
Standard D97-66, "Test for Pour Point of Petroleum Oils."
Figure: 30 TAC §115.10(45)
]
Subchapter B. GENERAL VOLATILE ORGANIC COMPOUND SOURCES
:
]
recovery
]
system, as defined in §115.10 of this title (relating to Definitions).
recovery
]
system, as defined in §115.10 of this title.
reduce total VOC emissions by
] at least
80%
[
30% from the bakery's 1990 baseline emissions inventory
]
by
December 31, 2001
[
May 31, 1996
].
reduce total VOC emissions by
] at least
80% [
from the bakery's 1990 baseline emissions inventory
] by December
31, 2000.
baseline
] emissions inventory in accordance with
the schedule specified in
§115.129(d)
[
§115.129(a)(4)
] of this title (relating to Counties and Compliance Schedules).
baseline
] emissions inventory
in accordance with the schedule specified in
§115.129(e)
[
§115.129(a)(5)
] of this title.
standard exemption
] required by Chapter 116
or Chapter 106 of this title (relating to Control of Air Pollution by Permits
for New Construction or Modification; and
Permits by Rule
[
Exemptions from Permitting
]). If
a permit by rule
[
a standard exemption
] is available for the project, compliance with
this subsection must be maintained for 30 days after the filing of documentation
of compliance with that
permit by rule
[
standard exemption
]; or
standard exemption
] is not
required for the project, the owner
or
[
/
] operator
has given the executive director 30 days' notice of the project in writing.
recovery
]
system, as defined in §115.10 of this title.
:
]
recovery
]
system, as defined in §115.10 of this title, with a control efficiency
of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry
basis corrected to 3.0% oxygen for combustion devices).
recovery
]
system, as defined in §115.10 of this title, with a control efficiency
of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry
basis corrected to 3.0% oxygen for combustion devices).
recovery
]
system, as defined in §115.10 of this title, with a control efficiency
of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry
basis corrected to 3.0% oxygen for combustion devices).
recovery
]
system, as defined in §115.10 of this title, with a control efficiency
of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry
basis corrected to 3.0% oxygen for combustion devices).
(a)
]
For the Beaumont/Port Arthur, Dallas/Fort Worth,
El Paso, and Houston/Galveston areas, compliance with §115.121(a) of
this title (relating to Emission Specifications)
] shall be determined
by applying
one or more of
the following test methods
and
procedures
, as appropriate
.
[
:
]
(1)
]
For flares,
Test
Method 22 (40
CFR
[
Code of Federal Regulations
] 60,
Appendix A)
is used
for visual determination of fugitive emissions
from material sources and smoke emissions
.
[
from flares;
]
(2)
]
For flares,
additional
test method requirements
are
[
for flares
] described
in 40
CFR
[
Code of Federal Regulations
] 60.18(f)
.
[
;
]
(3)
(4)
(5)
(6)
(7)
]
Minor modifications.
Minor
[
minor
] modifications to these test methods
may
be used, if
approved by the executive director.
(b)
(1)
(2)
(3)
(4)
(5)
(6)
(7)
(a)
]
For the Beaumont/Port
Arthur, Dallas/Fort Worth, El Paso, and Houston/ Galveston areas, the
]
owner or operator of any facility which emits volatile organic compounds (VOC)
through a stationary vent
in Aransas, Bexar, Calhoun, Matagorda, Nueces,
San Patricio, Travis, and Victoria Counties or in the Beaumont/Port Arthur,
Dallas/Fort Worth, El Paso, and Houston/Galveston areas
shall maintain
the following information
[
records
] at the facility for at
least two years
. The owner or operator
[
and
] shall make
the information
[
such records
] available
upon request
to representatives of the executive director, EPA, or any local air
pollution control agency having jurisdiction in the area [
upon request
]. [
These records shall include, but not be limited to, the following.
]
Records for each vent required to satisfy
] the provisions of
§115.121
[
§115.121(a)(1)-(3)
] of this title (relating to Emission
Specifications)
, records of appropriate parameters to demonstrate compliance,
[
shall be sufficient to demonstrate the proper functioning of
applicable control equipment to design specifications,
] including:
(B)
] [
continuous monitoring
of
]
the inlet and outlet gas
temperatures [
upstream
and downstream
] of a catalytic incinerator or chiller;
(C)
] [
continuous monitoring
of
] the exhaust gas VOC concentration of any carbon adsorption system,
as defined in §101.1 of this title (relating to Definitions);
and
(D)
]
of any vent
] conducted [
at an affected facility
] in accordance with [
the provisions specified
in
]
§115.125
[
§115.125(a)
] of this title
(relating to Testing Requirements).
(2)
]
Records for exempted vents.
Records for each vent exempted from control requirements in accordance
with
§115.127
[
§115.127(a)
] of this title
(relating to Exemptions) shall be sufficient to demonstrate compliance with
applicable exemption limits, including:
true partial pressure
] of VOC in each vent gas stream on a daily basis
.
[
; and
]
(D)
(3)
]
Alternative records for
exempted vents.
As an alternative to the requirements of paragraph
(3)
[
(2)
] of this
section
[
subsection
],
records for each vent exempted from control requirements in accordance with
§115.127
[
§115.127(a)
] of this title and having
a VOC emission rate or concentration less than 50% of the applicable exemption
limits at maximum actual operating conditions shall be sufficient to demonstrate
continuous compliance with the applicable exemption limit. These records shall
include complete information from either test results or appropriate calculations
which clearly documents that the emission characteristics at maximum actual
operating conditions are less than 50% of the applicable exemption limits.
This documentation shall include the operating parameter levels that occurred
during any testing, and the maximum levels feasible for the process.
(4)
]
Bakeries.
For bakeries
subject to
[
affected by
] §115.122(a)(3)(A) - (B) of
this title (relating to Control Requirements), the following additional requirements
apply.
(A)
(B)
(i)
(ii)
(C)
] All representations in [
initial
] control plans [
and annual reports
] become enforceable
conditions. It shall be unlawful for any person to vary from such representations
if the variation will cause a change in the identity of the specific emission
sources being controlled or the method of control of emissions unless the
owner or operator of the bakery submits a revised control plan to the executive
director, the appropriate regional office, and any local air pollution control
program with jurisdiction within 30 days of the change. All control plans
[
and reports
] shall include documentation that the overall
emission
reduction
from the uncontrolled VOC emission rate of the
bakery's oven(s)
[
of VOC emissions from the bakery's 1990 baseline
emissions inventory
] continues to be at least
the specified percentage
reduction
[
30%
]. The emission rates shall be calculated in
a manner consistent with the
most recent
[
1990
] emissions
inventory.
(5)
]
Bakeries (contingency
measures).
For bakeries
subject to
[
affected by
] §115.122(a)(3)(C)
and (D) of this title, the following additional requirements apply.
§115.129(a)(4)
] of
this title (relating to Counties and Compliance Schedules), the owner or
operator of each bakery shall submit an initial control plan to the executive
director, the appropriate regional office, and any local air pollution control
program with jurisdiction which demonstrates that the overall reduction of
VOC emissions from the bakery's 1990 [
baseline
] emissions inventory
will be at least 30%. At a minimum, the control plan shall include the EPN
and the FIN of each bakery oven and any associated control device, a plot
plan showing the location, EPN, and FIN of each bakery oven and any associated
control device, and the 1990 VOC emission rates (consistent with the bakery's
1990 emissions inventory). The projected VOC emission rates shall be calculated
in a manner consistent with the 1990 emissions inventory.
baseline
] emissions inventory during the
preceding calendar year is at least 30%. At a minimum, the report shall include
the EPN and FIN of each bakery oven and any associated control device, a plot
plan showing the location, EPN, and FIN of each bakery oven and any associated
control device, and the VOC emission rates. The emission rates for the proceeding
calendar year shall be calculated in a manner consistent with the 1990 emissions
inventory.
initial
] control plans
and annual reports become enforceable conditions. It shall be unlawful for
any person to vary from such representations if the variation will cause a
change in the identity of the specific emission sources being controlled or
the method of control of emissions unless the owner or operator of the bakery
submits a revised control plan to the executive director, the appropriate
regional office, and any local air pollution control program with jurisdiction
within 30 days of the change. All control plans and reports shall include
documentation that the overall reduction of VOC emissions from the bakery's
1990 [
baseline
] emissions inventory continues to be at least 30%.
The emission rates shall be calculated in a manner consistent with the 1990
emissions inventory.
(6)
]
Additional flare requirements.
The owner or operator of a facility that uses a flare to meet the requirements
of §115.122(a)(2)
of this title
shall install, calibrate,
maintain, and operate according to the manufacturer's specifications, a heat-sensing
device, such as an ultraviolet beam sensor or thermocouple, at the pilot light
to indicate continuous presence of a flame.
(b)
For Victoria County, the owner or operator
of any facility which emits VOC through a stationary vent shall maintain records
at the facility for at least two years and shall make such records available
to representatives of the executive director, EPA, or any local air pollution
control agency having jurisdiction in the area upon request. These records
shall include, but not be limited to, the following.
]
(1)
(A)
(B)
(C)
(D)
(2)
(A)
(B)
(C)
(D)
(3)
0.009 pounds per square inch absolute (psia) true
partial pressure (612 parts per million (ppm))
];
0.44 psia true partial pressure (30,000 ppm)
];
0.009 pounds psia true partial pressure (612 ppm))
];
and
0.006 psia true partial pressure
(408 ppm)
].
parts per million
by volume
] is exempt from the requirements of §115.121(a)(2)(A)
of this title.
0.44 psia true partial pressure (30,000 ppm)
].
0.44 psia true partial pressure (30,000 ppm)
].
All affected persons in the Beaumont/Port Arthur, Dallas/Fort
Worth, El Paso, and Houston/Galveston areas shall be in compliance with this
undesignated head (relating to Vent Gas Control) in accordance with the following
schedules:
]
(1)
(2)
]
The owner or operator
of each bakery
[
All affected bakeries
] in Brazoria, Chambers,
Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties shall
comply
[
be in compliance
] with §§115.121(a)(3),
115.122(a)(3),
and 115.126(5)
[
115.126(a)(4), and 115.127(a)(5)
] of this title (relating to Emission Specifications; Control Requirements;
and
Monitoring and Recordkeeping Requirements [
; and Exemptions
]) as soon as practicable, but no later than
December 31, 2001
[
May 31, 1996
].
(3)
]
The owner or operator
of each bakery
[
All bakeries
] in Collin, Dallas, Denton,
and Tarrant Counties
subject to
[
affected by
] §115.122(a)(3)(B)
of this title shall
comply
[
be in compliance
] with §§115.121(a)(3),
115.122(a)(3),
and 115.126(5)
[
115.126(a)(4), and 115.127(a)(5)
] of this title as soon as practicable, but no later than
December
31, 2000
[
May 31, 1996
].
(4)
]
The owner or operator
of each bakery
[
All bakeries
] in Collin, Dallas, Denton,
and Tarrant Counties
subject to
[
affected by
] §115.122(a)(3)(C)
of this title shall
comply
[
be in compliance
] with §§115.121(a)(3),
115.122(a)(3)(C),
and 115.126(6)
[
115.126(a)(5), and 115.127(a)(5)
] of this title as soon as practicable, but no later than one year,
after the commission publishes notification in the
Texas Register
of its determination that this contingency rule is necessary
as a result of failure to attain the national ambient air quality standard
(NAAQS) for ozone by the attainment deadline or failure to demonstrate reasonable
further progress as set forth in the
FCAA
[
1990 Amendments
to the Federal Clean Air Act (FCAA)
], §172(c)(9).
(5)
]
The owner or operator
of each bakery
[
All bakeries
] in El Paso County
subject
to
[
affected by
] §115.122(a)(3)(D) of this title shall
comply
[
be in compliance
] with §§115.121(a)(3),
115.122(a)(3)(D),
and 115.126(6)
[
115.126(a)(5), and 115.127(a)(5)
] of this title as soon as practicable, but no later than one year,
after the commission publishes notification in the
Texas Register
of its determination that this contingency rule is necessary
as a result of failure to attain the NAAQS for ozone by the attainment deadline
or failure to demonstrate reasonable further progress as set forth in [
the 1990 Amendments to
] the FCAA, §172(c)(9).
6.
BATCH PROCESSES
area
], as defined in §115.10 of this title (relating
to Definitions), under the following Standard Industrial Classification (SIC)
codes:
area
] shall comply
with the following control requirements.
area
] shall determine
the mass emissions and flow rates as follows.
area
] shall comply
with the following.
area
] shall maintain
the following information for at least two years at the plant, as defined
by its air quality account number. The owner or operator shall make the information
available upon request to representatives of the executive director, EPA,
or any local air pollution control agency having jurisdiction in the area:
volatile organic compounds
(VOC) transfer
] operations, records of appropriate parameters to demonstrate
compliance, including:
VOC
] exiting the recovery device based on a detection
principle such as infrared, photoionization, or thermal conductivity;
in the Beaumont/Port Arthur area
].
100 tons per year
] from all stationary emission sources included
in the account are exempt from the requirements of this division (relating
to Batch Processes), except for §115.161(b) of this title (relating to
Applicability)
:
[
.
]
Subchapter C. VOLATILE ORGANIC COMPOUND TRANSFER OPERATIONS
and gasoline
bulk plant
] in the covered attainment counties and in the Beaumont/Port
Arthur, Dallas/Fort Worth, El Paso, and Houston/Galveston areas, as defined
in §115.10 of this title (relating to Definitions), shall ensure that
volatile organic compound (VOC) emissions from the vapor control system vent
at gasoline terminals do not exceed the following rates:
loading and
unloading of
] VOC
transfer to or from transport vessels
shall
be conducted such that:
loading and
unloading of
] VOC
transfer to or from transport vessels
shall
be conducted such that:
(relating to Inspection Requirements)
].
4.
CONTROL OF VEHICLE REFUELING EMISSIONS (STAGE II) AT MOTOR VEHICLE FUEL DISPENSING FACILITIES
Subchapter E. SOLVENT-USING PROCESS
4.
OFFSET LITHOGRAPHIC PRINTING
(d)
] In Brazoria, Chambers, Fort
Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, all offset
lithographic printing presses
on a property which, when uncontrolled,
emit a combined weight of VOC less than 25 tons per calendar year,
shall
be in compliance with §§115.442, 115.443, 115.445, and 115.446 of
this title as soon as practicable, but no later than one year, after the commission
publishes notification in the
Texas Register
of its determination that this contingency rule is necessary as a result of
failure to attain the NAAQS for ozone by the attainment deadline or failure
to demonstrate reasonable further progress as set forth in [
the 1990
Amendments to
] the FCAA, §172(c)(9).
Subchapter J. ADMINISTRATIVE PROVISIONS
Emissions Trading
].
(a)
or
] discrete emission reduction credits
(DERCs), or
mobile discrete emission reduction credits (MDERCs)
in accordance with
this section and Chapter 101, Subchapter H, Division 1 of this title (relating
to Emission Credit Banking and Trading) or Chapter 101, Subchapter H, Division
4 of this title (relating to Discrete Emission Reduction Banking and Trading).
For the purposes of this section, the term "RC" refers to an ERC, MERC, DERC,
or MDERC, whichever is applicable.
[
§101.29 of this title
(relating to Emission Credit Banking and Trading)
].
Chapter 117.
CONTROL OF AIR POLLUTION FROM NITROGEN COMPOUNDS