Part 1.
TEXAS COMMISSION ON ENVIRONMENTAL QUALITY
Chapter 101.
GENERAL AIR QUALITY RULES
Subchapter H. EMISSIONS BANKING AND TRADING
6.
HIGHLY-REACTIVE VOLATILE ORGANIC COMPOUND EMISSIONS CAP AND TRADE PROGRAM
30 TAC §§101.390 - 101.394, 101.396, 101.399 - 101.401, 101.403
The Texas Commission on Environmental Quality (commission)
proposes new §§101.390 - 101.394, 101.396, 101.399 - 101.401, and
101.403. These new sections are being proposed in Subchapter H, Emissions
Banking and Trading, new Division 6, Highly-Reactive Volatile Organic Compound
Emissions Cap and Trade Program.
The new sections are proposed to be submitted to the United States Environmental
Protection Agency (EPA) as revisions to the state implementation plan (SIP).
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES
The Houston/Galveston ozone nonattainment area (HGA) is classified as Severe-17
under the Federal Clean Air Act Amendments of 1990 (as codified in 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 (125 parts per billion) by November 15, 2007. The HGA consists
of Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery,
and Waller Counties, and the commission has been working to develop a demonstration
of attainment in accordance with 42 USC, §7410. The most relevant HGA
SIP revisions to date are the December 2000 one-hour ozone standard attainment
demonstration, the September 2001 follow-up revision, and the December 2002
nitrogen oxides (NO
x
)/highly-reactive volatile
organic compound (HRVOC) revision.
This process has proven to be extremely challenging due to the magnitude
of reductions needed for attainment. The emission reduction requirements included
as part of the December 2000 SIP revision represent substantial, intensive
efforts on the part of stakeholder coalitions in the HGA, in partnership with
the commission, to address ozone. These coalitions include local governmental
entities, elected officials, environmental groups, industry, consultants,
and the public, as well as the EPA and the commission, who have worked diligently
to identify and quantify control strategy measures for the HGA attainment
demonstration.
December 2000
The December 2000 SIP revision contained rules and photochemical modeling
analyses in support of the HGA ozone attainment demonstration. The majority
of the emissions reductions identified in this revision were from a 90% reduction
in point source NO
x
. The modeling analysis also
indicated a shortfall in necessary NO
x
emission
reductions, such that an additional 91 tons per day (tpd) of NO
x
reductions were necessary for an approvable attainment demonstration.
In addition, the revision contained post-1999 rate-of-progress (ROP) plans
for the milestone years 2002 and 2005 and for the attainment year 2007, and
transportation conformity motor vehicle emissions budgets (MVEB) for NO
September 2001
The September 2001 SIP revision for the HGA included the following elements:
1) corrections to the ROP table/budget for the years 2002, 2005, and 2007
due to a mathematical inconsistency; 2) incorporation of a change to the idling
restriction control strategy to clarify that the operator of a rented or leased
vehicle is responsible for compliance with the requirements in situations
where the operator of a leased or rented vehicle is not employed by the owner
of the vehicle (the commission committed to making this change when the rule
was adopted in December 2000); 3) incorporation of revisions to the clean
diesel fuel rules to provide greater flexibility for compliance with the requirements
of the rule while preserving the emission reductions necessary to demonstrate
attainment in the HGA; 4) incorporation of a stationary diesel engine rule
that was developed as a result of the state's analysis of EPA's reasonably
available control measures; 5) incorporation of revisions to the point source
NO
x
rules; 6) incorporation of revisions to the
emissions cap and trade rules; 7) removal of the construction equipment operating
restriction and the accelerated purchase requirement for Tier 2/3 heavy-duty
equipment; 8) replacement of these rules with the Texas Emission Reduction
Plan program; 9) layout of the midcourse review process that details how the
state will fulfill the commitment to obtain the additional emission reductions
necessary to demonstrate attainment of the one-hour ozone standard in the
HGA; and 10) replacement of 2007 ROP MVEBs to be consistent with the attainment
MVEBs.
As was discussed in the December 2000 revision, the modeling resulted in
a 141 parts per billion peak ozone level that correlated to a shortfall calculation
of 91 tpd NO
x
equivalent emissions. An additional
five tpd were added to the shortfall, because the state could not take credit
for the NO
x
reductions associated with the diesel
pull-ahead strategy. The excess emissions from this strategy were not included
in the original emissions inventory. The gap control measures adopted in December
2000, along with the stationary diesel engine rules included in the September
2001 revision, resulted in NO
x
reductions of
40 tpd, which left a total remaining shortfall of 56 tpd. The state committed
to address this shortfall through the midcourse review process.
December 2002
In January 2001, the Business Coalition for Clean Air - Appeal Group and
several regulated companies challenged the December 2000 HGA SIP and some
of the associated rules. Specifically, the Business Coalition for Clean Air
- Appeal Group challenged the 90% NO
x
reduction
requirement from stationary sources in the HGA. In May 2001, the parties agreed
to a stay in the case, and Judge Margaret Cooper, Travis County District Court,
signed a consent order, effective June 8, 2001, requiring the commission to
perform an independent, thorough analysis of the causes of rapid ozone formation
events and identify potential mitigating measures not yet identified in the
HGA attainment demonstration, according to the milestones and procedures in
Exhibit C (Scientific Evaluation) of the order.
In compliance with the consent order, the commission conducted a scientific
evaluation based in large part on aircraft data collected by the Texas 2000
Air Quality Study (TexAQS). The TexAQS, a comprehensive research project conducted
in August and September 2000 involving more than 40 research organizations
and over 200 scientists, studied ground-level ozone air pollution in the HGA
and east Texas regions. The study revealed that while industrial source NO
To address these findings and to fulfill obligations in the consent order,
the commission adopted a SIP revision in December 2002 that focused on replacing
the most stringent 10% industrial NO
x
reductions
with VOC controls. In light of the TexAQS study, the commission conducted
further modeling analysis of ambient VOC data. The results of photochemical
grid modeling and analysis indicated that the same level of air quality benefits
achieved with a 90% industrial NO
x
emissions
reduction could be achieved with an overall 80% industrial NO
x
emissions reduction when combined with an industrial VOC emissions
reduction. This conclusion was based on results from several studies, including
photochemical grid modeling of the August - September 2000 episode using a
top-down emissions inventory adjustment to point source HRVOC emissions, and
analyses of ambient HRVOC measurements made by commission automated gas chromatographs
and airborne canisters using the maximum incremental reactivity and hydroxyl
reactivity scales. Four HRVOCs (ethylene, propylene, 1,3-butadiene, and butenes)
clearly play important roles in the HGA ozone formation, and these four are
the best candidates for the first round of HRVOC controls.
In order to address these scientific findings, the commission adopted revisions
to the industrial source control requirements, one of the control strategies
within the existing federally approved SIP. The December 2002 revision contains
new rules to reduce HRVOC emissions from four key industrial sources: fugitives,
flares, process vents, and cooling towers. The adopted rules target HRVOCs
while maintaining the integrity of the SIP. Analysis showed that limiting
emissions of ethylene, propylene, 1,3-butadiene, and butenes in conjunction
with an 80% reduction in NO
x
is equivalent in
terms of air quality benefit to that resulting from a 90% point source NO
The technical support documentation accompanying the revision contains
the supporting analysis for early results from ongoing analysis examining
whether reductions in HRVOC emissions could replace the last 10% of industrial
NO
x
controls with a reduction of approximately
64% in industrial HRVOC emissions, while ensuring that the air quality specified
in the approved December 2000 HGA SIP is met.
Current SIP Revision
As mentioned previously, the commission committed to perform a midcourse
review to ensure attainment of the one-hour ozone standard. The midcourse
review process provides the ability to update emissions inventory data, utilize
current modeling tools, such as MOBILE6, and enhance the photochemical grid
modeling. The data gathered from the TexAQS continues to improve photochemical
modeling of the HGA. All of these technical improvements give a more comprehensive
understanding of the ozone challenge in the HGA that is necessary to develop
an attainment plan. In the early part of 2003, the commission was preparing
to move forward with the midcourse review; however, during the same time period
the EPA announced its plans to begin implementation of the eight-hour ozone
standard. The EPA published proposed rules for implementation of the eight-hour
ozone standard in the June 2, 2003 issue of the
Federal Register
(68 FR 32802). In the same time frame, EPA also formalized
its intentions to designate areas for the eight-hour ozone standard by April
15, 2004, meaning that states would need to reassess their efforts and control
strategies to address this new standard by 2007. Recognizing that existing
one-hour nonattainment areas would soon be subject to the eight-hour ozone
standard, and in an effort to efficiently manage the state's limited resources,
the commission decided to develop an approach that addresses the outstanding
obligations under the one-hour ozone standard while beginning to analyze eight-hour
ozone issues.
The commission's one-hour ozone SIP commitments include: 1) completing
a one-hour ozone midcourse review; 2) performing modeling; 3) adopting measures
sufficient to fill the NO
x
shortfall; 4) adopting
measures sufficient to demonstrate attainment; and 5) revising the MVEB using
MOBILE6.
Results from the TexAQS and recent photochemical modeling indicate that
additional HRVOC reductions would be the most beneficial measure in reducing
ozone in the HGA. The commission is proposing to reduce HRVOC emissions to
reach attainment of the one-hour ozone standard. The photochemical modeling
of the August - September 2000 episode coupled with a weight-of-evidence argument
demonstrates attainment of the one-hour ozone standard. To achieve the necessary
HRVOC reductions, the commission is proposing a two-pronged approach that
would address variable short-term emissions through a not-to-exceed limit,
and would address steady state and routine emissions through an annual cap.
The annual HRVOC cap in Harris County would be reduced from the existing HRVOC
cap in order to support the attainment demonstration modeling. The annual
HRVOC cap in the seven-county surrounding area is equivalent to the total
emissions limits established in the December 2002 revision, but represented
on an annual basis instead of a 24-hour rolling average. The commission will
continue to evaluate the necessity to require short-term and annual reductions
from those sites subject to Chapter 115, Subchapter H, Divisions 1 and 2,
that are located within the seven-county surrounding area. If the evaluation
demonstrates that reductions from these counties have little impact on attainment
of the one-hour ozone standard, the short-term and annual limits for those
other seven counties within HGA may no longer be required.
The annual cap emissions would be distributed and enforced through an HRVOC
emissions cap and trade program through Subchapter H, Division 6 of Chapter
101. This program would establish a mandatory annual HRVOC emission cap on
all sites located in the HGA that have the potential to emit more than ten
tpy of HRVOC and that are subject to the HRVOC control requirements of 30
TAC Chapter 115, Subchapter H, Division 1, Vent Gas Control, or Division 2,
Cooling Tower Heat Exchange Systems. The cap would be enforced by the allocation,
trading, and banking of allowances. An allowance is the equivalent of one
ton of HRVOC emissions. This HRVOC cap would be established at levels demonstrated
as necessary to allow the HGA to attain the one-hour ozone standard. The proposed
cap would initially be implemented on April 1, 2006. These proposed sections
would also require all sites with new or modified HRVOC sources in the HGA
to obtain unused allowances from other sites already participating under the
cap for any increased HRVOC emissions. For sites that have the potential to
emit ten tons per year (tpy) or less of HRVOC from sources subject to the
HRVOC control requirements of Chapter 115, Subchapter H, Divisions 1 or 2,
the total, aggregate HRVOC emissions from those sources would be limited to
ten tpy. Sites exempt from the HRVOC emissions cap and trade program would
be extended an opportunity to opt-in, receive an HRVOC allocation, and thereby
not be restricted to the ten tpy limit.
The HGA SIP no longer relies solely on NO
x
-based
strategies. A combination of point source HRVOC controls and NO
x
reductions appear to be the most effective means of reducing ozone
in the HGA and there is no longer a NO
x
shortfall
in the HGA SIP. The commission also evaluated a number of the existing control
strategies that were put in place in the December 2000 revision. The photochemical
modeling shows that some of these strategies are no longer necessary to attain
the one-hour ozone standard. This SIP revision is proposing the repeal of
the commercial lawn and garden equipment restrictions, the repeal of the heavy-duty
vehicle idling restrictions, and the removal of the motor vehicle inspection
and maintenance program requirements from Chambers, Liberty, and Waller Counties.
In addition, this SIP proposal includes revisions to the environmental speed
limit strategy. In September 2002, the commission revised the existing speed
limit strategy to suspend the 55 mile per hour (mph) speed limit until May
1, 2005, and, where posted speeds were 65 mph or higher before May 1, 2002,
to increase speed limits to five mph below what was posted. The 78th Legislature,
2003, removed the commission's authority to determine speed limits for environmental
purposes; therefore, this proposal would remove the reinstatement of the 55
mph speed limit on May 1, 2005, and would maintain the currently posted speed
limits at five mph below the posted limit before May 1, 2002. Also, as part
of this SIP revision, the commission is proposing new statewide portable fuel
container rules. Historically, the commission has expressed a preference to
implement technology-based strategies over behavior-altering strategies, and
these proposed changes embody that philosophy.
Through this revision, the commission is fulfilling its outstanding one-hour
ozone SIP obligations and beginning to plan for the upcoming eight-hour ozone
standard. This proposal demonstrates attainment of the one-hour ozone standard
in the HGA in 2007 and provides a preliminary analysis of the HGA in terms
of the eight-hour ozone standard in 2007 and 2010. EPA's proposed eight-hour
implementation rules provide flexibility to the states in transitioning from
the one-hour to the eight-hour ozone standard, and the commission believes
the steps taken in this proposal and the technical work performed to date
will be invaluable through the transition period. Upon EPA's finalization
of the eight-hour implementation and the transportation conformity rules,
the commission expects to begin developing eight-hour ozone SIPs.
This is to put all interested parties on notice that, although the commission
is proposing the following rules, including a cap and trade program and a
short-term limit on HRVOC emissions, the commission may significantly amend
these proposed rules at adoption, repropose a portion of these rules, or propose
additional rules, as appropriate.
First, the commission continues to analyze the rules for implementation
of the eight-hour ozone standard adopted by EPA on April 15, 2004. These rules
and their preamble suggest that a demonstration of attainment of the one-hour
ozone standard may not be required for the portion of the SIP pertaining to
the HGA. This means that the commission will need to review the measures contained
in the current proposal to ensure that they are needed in this form in order
to demonstrate noninterference. Additional analysis of the impact of the proposed
rules on attainment of the eight-hour standard may indicate a need for new
or more stringent control measures and could result in the modification of
the HRVOC emissions caps established under this proposed rule.
Second, the commission may determine that, if a one-hour attainment demonstration
is necessary, additional, different, or more stringent control measures may
be needed based on additional modeling. The commission staff continues to
model scenarios under the one-hour standard, and the commission may determine
that the results indicate a need for changes in control strategies. Moreover,
the one-hour attainment demonstration includes a weight-of-evidence argument.
Additional review of the issues relating to the weight-of-evidence argument
could lead the commission to propose new strategies or to repropose the control
strategies proposed today.
SECTION BY SECTION DISCUSSION
Section 101.390, Definitions
The proposed new §101.390 would contain the definitions to be used
with the proposed new HRVOC emissions cap and trade program. The definition
of "Allowance" would be the authorization to emit 1/10 ton of HRVOC 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
that is not used to reconcile emissions in the designated year of allocation,
but 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 "Level of activity" would be the amount of HRVOCs
in pounds produced as an intermediate, by-product, or final product or used
by a process unit during a given period of time, but excluding any recycled
HRVOCs internal to the process unit. The definition of "Petroleum refinery"
would be the collection of process units used at a site primarily engaged
in petroleum refining as defined in the North American Industrial Classification
System for Petroleum Refining (324110). For the purposes of this subchapter,
a petroleum refinery process unit refers only to those process units located
at sites that do not include process units that produce ethylene except as
a by-product. The definition of "Process unit" would be a collection of equipment
assembled and connected by hardpiping or duct work, used to process a raw
material or intermediate in the manufacture or production of a final product.
The new division refers to the following predefined definitions: "Cooling
tower heat exchange system" as defined in 30 TAC §115.760; "Flare" as
defined in 30 TAC §101.1; "Houston/Galveston (HGA) ozone nonattainment
area" as defined in §101.1; "HRVOC" as defined in 30 TAC §115.10;
"Site" as defined by 30 TAC §122.10; and "Vent" as defined in §101.1.
Section 101.391, Applicability
The proposed new §101.391 would state that the requirements of Division
6 apply to each site located in the HGA that is subject to the HRVOC requirements
of Chapter 115, Subchapter H, Division 1 or 2 and the types of facilities
covered. The proposed new §101.391 would also state that any site that
elects to opt-in to this division under §101.392(b), Exemptions, would
always be subject to the program.
Section 101.392, Exemptions
The proposed new §101.392 would exempt from this division any site
meeting the applicability requirements of §101.391 with the potential
to emit ten tpy or less of HRVOC from all covered facilities at the site.
For the purpose of determining exemption status, the site's potential to emit
HRVOC from all covered facilities would be compared to the ten tpy exemption
level for each year of operation beginning with calendar year 2000. If at
any time the site's potential to emit exceeds the ten tpy exemption level,
the site would be subject to the HRVOC emissions cap and trade program. Once
subject to the HRVOC cap and trade program, a site would always be subject
to the program. Sites exempt from this division would be extended an opportunity
to opt-in to the HRVOC emissions cap and trade program. Notification of a
site's election to opt-in to the requirements of this division would be required
in writing to the executive director no later than April 30, 2005.
Section 101.393, General Provisions
The proposed new §101.393 would state that allowances may only be
used to meet the requirements of Division 6 and cannot be used to meet or
exceed the limitations of any annual emission limitation established under
30 TAC 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 set the initial control period as
April 1, 2006 through December 31, 2006 with each control period thereafter
beginning on January 1 and ending on December 31. The new section would require
each site subject to this division to hold a quantity of allowances in its
compliance account equal to or greater than its total HRVOC emissions from
all covered facilities during the previous control period. 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, Subchapter B, Division 7 but not for netting requirements.
The new section states that all allowances would be allocated, transferred,
deducted, or used in tenths of tons and that one compliance account shall
be used for each site. 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 and broker 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.
Section 101.394, Allocation of Allowances
The proposed new §101.394 describes how allowances would be allocated
to each site subject to this division. The executive director would allocate
allowances under this division on March 31, 2006. For sites subject to this
division that are located in Harris County, allowances would be allocated
for emissions of the following HRVOCs: 1,3-butadiene; all isomers of butene
(e.g., isobutene (2-methylpropene or isobutylene), alpha-butylene (ethylethylene)
and beta-butylene (dimethylethylene, including both cis- and trans- isomers));
ethylene; and propylene. Allowances would be allocated in the aggregate, not
specifically identified for each HRVOC species. Sites within Harris County
that would not receive an allocation under subsection (c) or (d) would receive
an allocation based on a percentage of the site's baseline level of activity
relative to the total baseline level of activity for all sites within Harris
County. This percentage would then be applied to the tons of HRVOC modeled
in the attainment demonstration for those sites within Harris County. For
sites subject to this division that are located in Brazoria, Chambers, Fort
Bend, Galveston, Liberty, Montgomery, and Waller Counties, allowances would
be allocated for emissions of the following HRVOCs: ethylene and propylene.
Allowances would be allocated in the aggregate, not specifically identified
for each HRVOC species. Sites within Brazoria, Chambers, Fort Bend, Galveston,
Liberty, Montgomery, and Waller Counties that would not receive an allocation
under subsection (c) or (d) would receive an allocation based on a percentage
of the site's baseline level of activity relative to the total baseline level
of activity for all sites within those counties. This percentage would then
be applied to the tons of HRVOC modeled in the attainment demonstration for
those sites within Brazoria, Chambers, Fort Bend, Galveston, Liberty, Montgomery,
and Waller Counties. The level of activity baseline for a site would be calculated
as the average annual level of activity for the five consecutive year period
of calendar years 2000 through 2004. For the five-year period, the level of
activity would be determined by summing the levels of activity for all process
units located at the site that produce one or more HRVOCs as an intermediate,
by-product, or final product or that use one or more HRVOCs as a raw material
or intermediate to produce a product. New sites or sites that become subject
to this division at a later date by increasing HRVOC emissions above the exemption
level would be required to obtain allowances from other sites already participating
in the cap and trade program.
Sites subject to this division that do not include process units that produce
or use an HRVOC would receive an allocation based on HRVOC throughput or storage
capacity for the five consecutive year period between calendar years 2000
through 2004. Examples of facilities that do not produce or use HRVOCs include
storage facilities or pipelines. Up to 10% of the total HRVOC emissions for
Harris County would be equitably allocated to those sites within Harris County
subject to this division but that do not include process units that produce
or use an HRVOC. Likewise, up to 10% of the total HRVOC emissions for Brazoria,
Chambers, Fort Bend, Galveston, Liberty, Montgomery, and Waller Counties would
be equitably allocated to sites in those counties meeting the same qualifications.
In order to be allocated allowances from this set-aside, owners or operators
of sites subject to this division that do not include process units that produce
or use an HRVOC would be required to apply to the executive director no later
than January 30, 2005. Allowances up to the full 10% not allocated to sites
meeting the previously mentioned criteria would be distributed proportionately
to those sites producing or using an HRVOC. The commission may evaluate the
distribution of any allowances remaining from this 10% that has been set aside
to sites that are newly constructed, and therefore, have not established a
baseline.
The commission proposes to allocate allowances to those process units that
are a part of a petroleum refinery independent of those process units that
are a part of a chemical plant or a petroleum refinery collocated with a chemical
plant. Because the commission's allocation process is based on HRVOC production
or use, the commission is segregating these refineries to an independent segment
of the emissions allocation. This segregation is based on the understanding
that HRVOC emissions from a refinery may be disproportionate to HRVOC emissions
from a chemical plant. As a part of the refining process, HRVOCs are produced
in the cracking of gas oil feedstocks into lower molecular weight hydrocarbons
and distributed throughout the refinery in various production units. The HRVOC
produced or used in a refinery may be associated with multiple emission points
resulting in a greater chance for the HRVOCs to escape controls while the
HRVOC produced or used in a chemical or olefins plant may be more typically
associated with fewer emission points and has greater potential to be present
in a concentrated stream and controlled at fewer emission points. Therefore
emissions from refineries may be disproportionate when basing allowance allocations
on HRVOC production use and versus chemical plants.
For petroleum refinery process units subject to this division that are
located in Harris County, allowances would be allocated for emissions of the
following HRVOCs: 1,3-butadiene; all isomers of butene (e.g., isobutene (2-methylpropene
or isobutylene), alpha-butylene (ethylethylene) and beta-butylene (dimethylethylene,
including both cis- and trans- isomers)); ethylene; and propylene. Allowances
would be allocated in the aggregate, not specifically identified for each
HRVOC species. Petroleum refineries within Harris County would receive an
allocation based on a percentage of the site's baseline level of activity
relative to the total baseline level of activity for all refinery process
units within Harris County. This percentage would then be applied to the tons
of HRVOC modeled in the attainment demonstration for those refinery units
within Harris County. For petroleum refinery process units subject to this
division that are located in Brazoria, Chambers, Fort Bend, Galveston, Liberty,
Montgomery, and Waller Counties, allowances would be allocated for emissions
of the following HRVOCs: ethylene and propylene. Allowances would be allocated
in the aggregate, not specifically identified for each HRVOC species. Petroleum
refineries within Brazoria, Chambers, Fort Bend, Galveston, Liberty, Montgomery,
and Waller Counties would receive an allocation based on a percentage of the
site's baseline level of activity relative to the total baseline level of
activity for all petroleum refineries within those counties. This percentage
would then be applied to the tons of HRVOC modeled in the attainment demonstration
for those sites within Brazoria, Chambers, Fort Bend, Galveston, Liberty,
Montgomery, and Waller Counties. The level of activity baseline for a site
would be calculated as the average annual level of activity for the five consecutive
year period between calendar years 2000 through 2004. For the five-year period,
the level of activity would be determined by summing the levels of activity
for all process units located at the site that produce one or more HRVOCs
as an intermediate, by-product, or final product or that use one or more HRVOCs
as a raw material or intermediate to produce a product.
The section states that if a site emits more HRVOC than what was held in
the compliance account on March 1 following a control period, that the allocation
for the next control period will be reduced by an amount equal to the emissions
exceeding the compliance account plus an additional 10%. For example, an emissions
exceedance of ten tons would result in a penalty reduction of 11 tons for
the next control period. If a compliance account does not have sufficient
allowances to accommodate the penalty reduction, it is the responsibility
of the owner or operator to purchase or transfer additional allowances within
30 days of the notice of deficiency from the executive director. Allowances
would be deposited initially by March 31, 2006 and subsequently by January
1 of each control period. To account for program implementation on April 1,
allocations for the 2006 control period would be reduced by 25% from the annual
allocation to be distributed in each control period thereafter. The annual
allocation of allowances may be adjusted to reflect any new or existing SIP
requirements. Allowances may be added or subtracted from a site's compliance
account in accordance with the annual reporting requirements in §101.400.
Proposed language would allow an owner or operator of a site to request that
the executive director approve the substitution of the level of activity from
one calendar year with the level of activity from the preceding or following
calendar year within the 2000 through 2004 time period due to extenuating
circumstances at the site. The executive director would only consider circumstances
not attributable to economic fluctuation.
Section 101.396, Allowance Deductions
The proposed new §101.396 describes how allowances would be deducted
from compliance accounts. On March 31 of the year following each control period,
allowances would be deducted from the site's compliance account equivalent
to the total HRVOC emissions from all covered facilities at the site. The
amount of HRVOC emissions would be required to be based on the monitoring
and testing protocols established in 30 TAC §115.725 and §115.764,
as appropriate for each process unit at the site. The section states that
annual HRVOC emissions from covered facilities would be calculated for each
hour of the year and summed to determine the total annual HRVOC emissions.
Emissions events subject to the requirements of 30 TAC §101.201 and emissions
from scheduled maintenance, startup, or shutdown activities subject to the
requirements of 30 TAC §101.211 would be required to be included in the
total annual HRVOC emissions for each control period. However, the hourly
emissions for emission events or emissions from scheduled maintenance, startup,
or shutdown activities to be included in the summation cannot exceed the short-term
limit of 30 TAC §115.722(c) and §115.761(c). This section would
also include a provision for missing data. Should the monitoring and testing
data required by this section be nonexistent or unavailable, a site would
be allowed to determine its HRVOC emissions using the following methods and
in the following order: continuous monitoring data; periodic monitoring data;
testing data; data from manufacturers; and engineering calculations. For sources
using continuous monitors to measure emissions, the last valid data point
from the monitor would be allowed to substitute for the missing data. A justification
would be required for sites using one of these alternate methods for determining
HRVOC emissions due to missing monitoring and testing data. The section states
that the executive director shall deduct allowances for compliance with a
control period beginning with the most recently allocated allowances prior
to deducting banked allowances.
Section 101.399, Allowance Banking and Trading
The proposed new §101.399 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. The section states that allowances that have not
expired or been used would be available for trade at any time after they have
been allocated. Trade requests involving allowances allocated for the current
control period or excess allowances from the previous control period would
be made through the submittal of a completed Form ECT-2, Application for Transfer
of Allowances. Persons receiving an annual allocation of HRVOC allowances
would be allowed to permanently transfer ownership of the current and future
allowances to be allocated to that site through the submittal of a completed
Form ECT-4, Application for Permanent Transfer of Allowance Ownership. Trades
involving the transfer of allowances scheduled to be allocated for a future
control period would be allowed through the submittal of a completed Form
ECT-5, Application for Transfer of Individual Future Year Allowances. With
the exception of transfers between sites under common ownership or control,
the account representative would be required to report the price paid per
allowance for all transfer transactions. All trades would be completed through
the executive director and would be considered final when the executive director
issues a letter to buyer and seller reflecting the transaction. Allowances
initially allocated to sites located in Harris County would be restricted
from use at sites located in Brazoria, Chambers, Fort Bend, Galveston, Liberty,
Montgomery, and Waller Counties. Allowances initially allocated to sites located
in Brazoria, Chambers, Fort Bend, Galveston, Liberty, Montgomery, and Waller
Counties would be restricted from use in Harris County. Only authorized account
representatives would be permitted to trade allowances. The section states
that allowances subject to an approved transaction would be deposited into
the purchaser's broker or compliance account within 30 days of receipt of
a completed transfer application.
Section 101.400, Reporting
The proposed new §101.400 states that sites shall submit a completed
HRVOC Emissions Cap and Trade Annual Compliance Report to the executive director
no later than March 31 following each control period detailing the amount
of actual HRVOC emissions for the preceding control period. The Annual Compliance
Report would be required to include the total amount of HRVOC emissions from
each covered facility at the site, the methods used in determining the HRVOC
emissions, and a summary of all final trades. The commission also proposes
to give the executive director authority to suspend trades involving the transfer
of allowances for future control periods from any site that has not submitted
an HRVOC Emissions Cap and Trade Annual Compliance Report. For example, if
after March 31, 2007, site A has not submitted an HRVOC Emissions Cap and
Trade Annual Compliance Report for the 2006 control period but has submitted
an application for transfer of 2003 allowances to site B, the trade would
be withheld pending the submittal of site A's HRVOC Emissions Cap and Trade
Annual Compliance Report and verification of compliance for 2006.
Section 101.401, Level of Activity Certification
The proposed new §101.401 states that all sites subject to this division
would be required to submit a completed Level of Activity Certification Form
certifying their baseline level of activity no later than April 30, 2005.
The Level of Activity Certification would include the level of activity for
all covered facilities at the site during the five consecutive year period
between calendar years 2000 through 2004. The Level of Activity Certification
would be required to include information and documentation in support of the
proposed level of activity baseline such as production, purchase, or usage
records. This information will be used to calculate each site's allocation.
The proposed section would allow an owner or operator to mark any portion
of the Level of Activity Certification Form and the supporting documentation
relating to HRVOC production or use as confidential under Texas Health and
Safety Code, §382.041.
Section 101.403, Program Audits and Reports
The proposed new §101.403 would require the executive director to
perform an audit of the HRVOC emissions cap and trade program within three
years of the effective date of the new division and every three years thereafter.
The audit would evaluate the impact of the program on the state implementation
plan, availability and cost of allowances, compliance by participants, necessity
for additional trading restrictions, and any other elements chosen by the
executive director. Additionally, no later than June 30 following each control
period, the executive director would be required to prepare and make available
a report for the previous control period. This report would detail the number
of allowances allocated to each compliance account, total number of allowances
allocated under this division, total amount of HRVOC allowances deducted from
each compliance account based on actual HRVOC emissions, and a summary of
all trades for the control period.
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT
Nina Chamness, Analyst, Strategic Planning and Grants Management Section,
determined that for the first five-year period the proposed rules are in effect,
there will be no significant fiscal impact to the agency or other units of
state and local government as a result of the administration or enforcement
of the proposed rules.
The proposed rules would establish a mandatory annual cap for HRVOC emissions
on all sites located in the HGA that emit, or have the potential to emit,
more than ten tpy of HRVOC and are subject to the HRVOC control requirements
for vent gas control or cooling tower heat exchange systems. The cap would
be enforced by the allocation, trading, and banking of allowances. An allowance
is the equivalent of one ton of HRVOC emissions. This HRVOC cap would be established
at levels necessary for the HGA to attain the national ambient air quality
standard (NAAQS) for the one-hour ozone standard. Unused allowances from one
site could be traded or sold to another site in the HGA. The proposed rules
would also require all sites with new or modified HRVOC sources in the HGA
to obtain unused allowances from other sites already participating under the
cap to offset any increased HRVOC emissions.
For sites that emit, or have the potential to emit, less than ten tons
of HRVOC per year from sources subject to the HRVOC control requirements for
vent gas control or cooling tower heat exchange systems, the total, aggregate
emissions from those sources would be limited to ten tpy of HRVOC. Sites exempt
from the HRVOC emissions cap and trade program would be extended an opportunity
to opt-in, receive an HRVOC allocation, and thereby not be restricted to the
ten tpy limit.
To implement the mandatory cap and allowance trading program, the agency
would have to perform oversight functions. Specifically, the commission's
Air Permits Division would allocate allowances, process allowance trades,
and review annual compliance reports as required by the proposed rules. These
tasks would be done by using existing resources within the Air Permits Division.
PUBLIC BENEFITS AND COSTS
Ms. Chamness also determined that for each year of the first five years
the proposed new rules are in effect, the public benefit anticipated will
be the reduction of ground-level ozone in the HGA to levels determined by
EPA as necessary for a healthy and safe environment.
There will be a significant impact on petrochemical, chemical, refinery,
storage, and loading companies located in the HGA ozone nonattainment area
that emit, or have the potential to emit, more than ten tpy of HRVOC and are
subject to the HRVOC control requirements for vent gas control or cooling
tower heat exchange systems. Approximately 150 sites will be subject to the
proposed rules. They would be required to submit a Level of Activity Certification
form to the agency no later than April 30, 2005. Compliance with the annual
cap and trade program would begin on April 1, 2006. By March 1 of each year,
sites would be required to possess a quantity of HRVOC allowances equivalent
to the previous year's actual HRVOC emissions. No later than March 31, 2007
and every March 31 for each year thereafter, sites would be required to submit
to the agency an Annual Compliance Report to demonstrate compliance with the
cap and trade program for the previous year.
Affected sites may incur significant costs related to the control of HRVOC
emissions or purchase of additional HRVOC allowances. Through the cap and
trade approach, sites would have the choice of controlling HRVOC emissions
or purchasing additional HRVOC allowances in order to meet their allowance
obligations. Costs may vary significantly depending on whether a site chooses
to control emissions or purchase allowances for compliance.
Because the commission does not know which methods companies will choose
to comply with the mandatory cap, it is unable to provide detailed cost estimates
for each site or process. However, the commission does have some estimated
cost information for particular devices and allowances that companies may
choose to utilize when complying with the cap. Based on fiscal information
provided in the 2002 HRVOC rule proposal, if a company wants to control HRVOC
emissions by installing an additional control device for previously uncontrolled
vent gas streams, the estimated capital and annual operating costs for such
a device could be approximately $600,000 and $360,000 respectively. If a company
chooses to purchase allowances, it may find that the costs of purchasing allowances
may vary significantly depending on their availability and the demand for
them. Also, no historical data for the price of trading allowances of HRVOCs
exists. The only available cost data is for NO
x
allowances.
The cost of allowances under the mass emissions cap and trade program for
NO
x
has historically yielded allowance prices
in the range of $100 to $200 per ton for a current year allowance and $40,000
per ton for a continuous stream of allowances. Affected industries would be
required to possess allowances equivalent to the actual HRVOC emissions from
the site.
SMALL BUSINESS AND MICRO-BUSINESS ASSESSMENT
The commission has been unable to identify any small or micro-businesses
that would be affected by the proposed rules. If there are affected small
or micro-businesses, the estimated capital and annualized cost in this fiscal
note could be a used as a cost estimate for small or micro-businesses.
LOCAL EMPLOYMENT IMPACT STATEMENT
The commission reviewed this proposed rulemaking and determined that a
local employment impact statement is not required because the proposed rules
do not adversely affect a local economy in a material way for the first five
years that the proposed rules are in effect.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the proposed rulemaking action 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. A "major environmental rule"
is 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, productivity, competition, jobs, the environment,
or the public health and safety of the state or a sector of the state.
The proposed rulemaking action to Chapter 101 and revisions to the SIP
would affect owners and operators of sources emitting HRVOC subject to Chapter
115, Subchapter H, Divisions 1 and 2. The rules are intended to protect the
environment and reduce risks to human health and safety from environmental
exposure and may have adverse effects on owners and operators of certain sources.
Many of these sources are owned or operated by utilities, petrochemical plants,
refineries, and other industrial, commercial, or institutional groups, and
each group could be considered a sector of the economy. This determination
is based on the analysis provided elsewhere in this preamble, including the
discussion in the PUBLIC BENEFITS AND COSTS section of this proposal.
This proposed rulemaking does not meet any of the four applicability criteria
of a "major environmental rule" as defined in the Texas Government Code. Section
2001.0225 applies only to a major environmental rule the result of which is
to: 1) exceed a standard set by federal law, unless the rule is specifically
required by state law; 2) exceed an express requirement of state law, unless
the rule is specifically required by federal law; 3) exceed a requirement
of a delegation agreement or contract between the state and an agency or representative
of the federal government to implement a state and federal program; or 4)
adopt a rule solely under the general powers of the agency instead of under
a specific state law.
The rulemaking implements requirements of 42 USC. Under 42 USC, §7410,
states are required to adopt a SIP that provides for "implementation, maintenance,
and enforcement" of the primary NAAQS in each air quality control region of
the state. While 42 USC, §7410, does not require specific programs, methods,
or reductions to meet the standard, 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, such as 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 to attain
the NAAQS for the specific regions in the state. Even though 42 USC allows
states to develop their own programs, this flexibility does not relieve a
state from developing a program that meets the requirements of 42 USC, §7410.
Thus, while specific measures are not generally required, the emission reductions
are required. States are not free to ignore the requirements of 42 USC, §7410,
and must develop programs to assure that the nonattainment areas of the state
will be brought into attainment on schedule.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code were amended by Senate Bill (SB) 633 during the
75th Legislature, 1997. The intent of SB 633 was to require agencies to conduct
an 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 discussed earlier
in this preamble, 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 in its fiscal notes. Because the legislature
is presumed to understand the fiscal impacts of the bills it passes, and that
presumption is based on information provided by state agencies and the Legislative
Budget Board, 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
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.
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
the HGA. The proposed rules, that will reduce ambient HRVOC and ozone in the
HGA, will be submitted to the EPA as one of several measures in the federally
approved SIP. As discussed earlier in this preamble, the banking and trading
scheme in the proposed rules are necessary to address some of the elevated
ozone levels observed in the HGA; this scheme will result in reductions in
ozone formation in the HGA and help bring the HGA into compliance with the
air quality standards established under federal law as NAAQS for ozone.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
The commission presumes that "when an agency interpretation is in effect at
the time the legislature amends the laws without making substantial change
in the statute, the legislature is deemed to have accepted the agency's interpretation."
As discussed, this rulemaking action implements requirements of 42 USC.
There is no contract or delegation agreement that covers the topic that is
the subject of this action. Therefore, the proposed rulemaking does not exceed
a standard set by federal law, exceed an express requirement of state law,
exceed a requirement of a delegation agreement, nor adopted solely under the
general powers of the agency. Finally, this rulemaking action was not developed
solely under the general powers of the agency, but is authorized by specific
sections of Texas Health and Safety Code, Chapter 382 (also known as the Texas
Clean Air Act), and Texas Water Code that are cited in the STATUTORY AUTHORITY
section of this preamble, including Texas Health and Safety Code, §§382.011,
382.012, 382.014, 382.016, 382.017, 382.021, and 382.034. Therefore, this
rulemaking action is not subject to the regulatory analysis provisions of
Texas Government Code, §2001.0225(b), because the proposed rulemaking
does not meet any of the four applicability requirements. The commission invites
public comment on the draft RIA determination.
TAKINGS IMPACT ASSESSMENT
The commission completed a takings impact assessment for this proposed
rulemaking action under Texas Government Code, §2007.043. The rules are
proposed as part of a strategy to reduce and permanently cap HRVOC emissions
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 rules do not affect private property in a manner
that 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,
this rulemaking action does not meet the definition of a takings under Texas
Government Code, §2007.002(5). 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 the 42 USC, §7410. Specifically,
the emission limitations and control requirements within these rules were
developed in order to meet the ozone NAAQS set by the EPA under the 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
this rulemaking action is to revise programs which provide flexibility in
meeting the ozone NAAQS set by the EPA under 42 USC, §7409. 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.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission determined that this rulemaking action relates to an action
or actions subject to the Texas Coastal Management Program (CMP) in accordance
with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources
Code, §§33.201
et seq
.), and the
commission rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency
with the CMP. As required by §281.45(a)(3) and 31 TAC §505.11(b)(2),
relating to Actions and Rules Subject to the Coastal Management Program, 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(l)).
No new sources of air contaminants will be authorized and the proposed rules
will maintain the same level of, or reduce the level of emissions as the existing
rules. The CMP policy applicable to this rulemaking action is the policy that
commission rules comply with federal regulations in 40 Code of Federal Regulations,
to protect and enhance air quality in the coastal areas (31 TAC §501.14(q)).
This rulemaking action complies with 40 Code of Federal Regulations Part 51,
Requirements for Preparation, Adoption, and Submittal of Implementation Plans.
Therefore, in accordance with 31 TAC §505.22(e), the commission affirms
that this rulemaking action is consistent with CMP goals and policies.
The commission solicits comments on the consistency of the proposed rulemaking
with the CMP during the public comment period.
EFFECT ON SITES SUBJECT TO THE FEDERAL OPERATING PERMITS PROGRAM
Because Chapter 101 contains applicable requirements under 30 TAC Chapter
122, Federal Operating Permits, owners or operators subject to the Federal
Operating Permit Program must, consistent with the revision process in Chapter
122, revise their operating permits to include the revised Chapter 101 requirements
for each emission unit at their site affected by the revisions to Chapter
101.
ANNOUNCEMENT OF HEARING
Public hearings for this proposed rulemaking have been scheduled for the
following times and locations: August 2, 2004, 1:30 p.m. and 5:30 p.m., City
of Houston, City Council Chambers, 2nd Floor, 901 Bagby, Houston; August 3,
2004, 10:30 a.m., John Gray Institute, 855 Florida Avenue, Beaumont; and August
5, 2004, 9:30 a.m., Texas Commission on Environmental Quality, 12100 North
I-35, Building F, Room 2210, Austin. The hearings will be structured for the
receipt of oral or written comments by interested persons. Registration will
begin 30 minutes prior to the hearings. Individuals may present oral statements
when called upon in order of registration. A time limit may be established
at the hearings to assure that enough time is allowed for every interested
person to speak. There will be no open discussion during the hearings; however,
commission staff members will be available to discuss the proposal 30 minutes
before the hearings and will answer questions before and after the hearings.
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
Comments may be submitted to Patricia Durón, MC 205, Texas Commission
on Environmental Quality, Office of Environmental Policy, Analysis, and Assessment,
P.O. Box 13087, Austin, Texas 78711-3087, or by fax to (512) 239-4808, or
emailed to
siprules@tceq.state.tx.us
. All
comments should reference Rule Project Number 2004-058-101-AI. Comments must
be received by 5:00 p.m., August 9, 2004. For further information, please
contact Cory Chism, Air Permits Division, (512) 239-0539 or Clifton Wise,
Policy and Regulations Division, (512) 239-2263.
STATUTORY AUTHORITY
The new sections are proposed under Texas Water Code, §5.103, concerning
Rules, and §5.105, concerning General Policy, that authorize the commission
to adopt rules necessary to carry out its powers and duties under the Texas
Water Code; and under Texas Health and Safety Code, §382.017, concerning
Rules, that authorizes the commission to adopt rules consistent with the policy
and purposes of the Texas Clean Air Act. The new sections are also proposed
under Texas Health and Safety Code, §382.002, concerning Policy and Purpose,
that establishes the commission purpose to safeguard the state air resources,
consistent with the protection of public health, general welfare, and physical
property; §382.011, concerning General Powers and Duties, that authorizes
the commission to control the quality of the state air; and §382.012,
concerning State Air Control Plan, that authorizes the commission to prepare
and develop a general, comprehensive plan for the control of the state air.
The new sections are also proposed under Texas Health and Safety Code, §382.014,
concerning Emission Inventory, that authorizes the commission to require a
person whose activities cause air contaminant emissions to submit information
to enable the commission to develop and emissions inventory; §382.016,
concerning Monitoring Requirements, that authorizes the commission to prescribe
reasonable requirements for the measuring and monitoring of air contaminant
emissions; and §382.051 and §382.0518, concerning Permitting Authority
of Commission and Preconstruction Permit, that authorize the commission to
issue preconstruction and operating air permits. The new sections are also
adopted under 42 USC, §7410(a)(2)(A), that requires SIPs to include enforceable
measures or techniques, including economic incentives such as fees, marketable
permits, and auction of emission rights.
The proposed new sections implement Texas Health and Safety Code, §§382.002,
382.011, 382.012, and 382.017; and House Bill 2912, §5.01 and §18.14,
77th Legislature, 2001.
§101.390.Definitions.
The following words and terms, when used in this division, have the
following meanings, unless the context clearly indicates otherwise.
(1)
Allowance--The authorization to emit one ton of highly-reactive
volatile organic compounds, expressed in tenths of a ton, during a control
period.
(2)
Authorized account representative--The responsible person
who is authorized in writing to transfer and otherwise manage allowances for
the site.
(3)
Banked allowance--An allowance that is not used to reconcile
emissions in the designated year of allocation, but is carried forward for
up to one year and noted as banked in the compliance account or broker account.
(4)
Broker--A person that is not required to participate in
the requirements of this division, but that 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 in which allowances held
by a site are recorded for the purposes of meeting the requirements of this
division.
(7)
Level of activity--The amount of highly-reactive volatile
organic compounds, as defined in §115.10 of this title (relating to Definitions),
in pounds produced as an intermediate, by-product, or final product or used
by a process unit during a given period of time, but excluding any recycled
highly-reactive volatile organic compounds internal to the process unit.
(8)
Petroleum refinery--A collection of process units used
at a site primarily engaged in petroleum refining as defined in the North
American Industry Classification System (324110). For the purposes of this
division, a petroleum refinery process unit refers only to those process units
located at sites that do not include process units that produce ethylene except
as a by-product.
(9)
Process unit--A collection of equipment assembled and connected
by hardpiping or duct work, used to process a raw material or intermediate
in the manufacture or production of a final product.
§101.391.Applicability.
This division applies to each site, as defined in §122.10 of this
title (relating to General Definitions), in the Houston/Galveston ozone nonattainment
area, as defined in §101.1 of this title (relating to Definitions), that
is subject to Chapter 115, Subchapter H, Division 1 of this title (relating
to Vent Gas Control) or Division 2 of this title (relating to Cooling Tower
Heat Exchange Systems). Covered facilities include all vent gas streams, flares,
and cooling tower heat exchange systems that emit highly-reactive volatile
organic compounds, as defined in §115.10 of this title (relating to Definitions),
and that are located at a site subject to Chapter 115, Subchapter H of this
title (relating to Highly-Reactive Volatile Organic Compounds). For the purpose
of compliance with Chapter 115, Subchapter H, Divisions 1 or 2 of this title,
each site that meets the applicability requirements of this section, or elects
to opt-in to this division under §101.392(b) of this title (relating
to Exemptions), shall always be considered to be subject to this division.
§101.392.Exemptions
(a)
Sites in the Houston/Galveston ozone nonattainment area
that have the potential to emit ten tons per year or less of highly-reactive
volatile organic compounds from all covered facilities at the site are exempt
from the requirements of this division.
(b)
Sites exempt from this division under subsection (a) of
this section may elect to opt-in to the requirements of this division by notifying
the executive director in writing by April 30, 2005.
§101.393.General Provisions.
(a)
Allowances may be used only for the purposes described
in this division and may not be used to meet or exceed the emission limitations
authorized under Chapter 116, Subchapter B of this title (relating to New
Source Review Permits), or any other applicable rule or law.
(b)
The initial control period is April 1, 2006 through December
31, 2006. Each control period after December 31, 2006 shall begin January
1 and end December 31 of each year. No later than March 1 after each control
period, a site subject to this division must hold a quantity of allowances
in its compliance account that is equal to or greater than the total highly-reactive
volatile organic compound emissions from the covered facilities located at
the site during the control period.
(c)
Allowances may not be used to satisfy netting requirements
under Chapter 116, Subchapter B, Divisions 5 and 6 of this title (relating
to Nonattainment Review; and Prevention of Significant Deterioration Review).
(d)
Allowances may be used simultaneously to satisfy the requirements
of this division and the one-to-one portion of the offset requirements for
new or modified covered facilities, subject to federal nonattainment new source
review requirements as provided in Chapter 116, Subchapter B, Division 7 of
this title (relating to Emission Reductions: Offsets).
(e)
An allowance does not constitute a security or a property
right.
(f)
All allowances will be allocated, transferred, deducted,
or used in tenths of tons. The number of allowances will be rounded down to
the nearest tenth of a ton when determining excess allowances and rounded
up to the nearest tenth of a ton when determining allowances used.
(g)
Each site shall have only one compliance account.
(h)
The commission will maintain a registry of compliance accounts
and broker accounts. The registry will not contain proprietary information.
§101.394.Allocation of Allowances
(a)
On March 31, 2006, the executive director will allocate
allowances as follows.
(1)
For sites located in Harris County that are not eligible
to receive allowances under subsection (c) or (d) of this section, allowances
for the emissions of one or more of the highly-reactive volatile organic compounds
(HRVOC) as defined in §115.10 of this title (relating to Definitions),
will be determined using the equation in the following figure.
(2)
For sites located in Brazoria, Chambers, Fort Bend, Galveston,
Liberty, Montgomery, and Waller Counties that are not eligible to receive
allowances under subsection (c) or (d) of this section, allowances for emissions
of ethylene and propylene for each site will be determined using the equation
in the following figure.
(b)
The level of activity of a site for a year shall be determined
by summing the levels of activity for all process units located at the site
that produce one or more HRVOCs as an intermediate, by-product, or final product
or that use one or more HRVOCs as a raw material or intermediate to produce
a product.
(c)
The owner or operator of a site that is subject to this
division, but that does not include a process unit that produces or uses an
HRVOC, shall apply by January 30, 2005 to the executive director for an allocation
based on HRVOC throughput or storage capacity for the five consecutive calendar
year period of 2000 through 2004.
(1)
The executive director may equitably allocate up to 10%
of the total HRVOC allocations for Harris County to all such sites located
in Harris County;
(2)
For sites located in Brazoria, Chambers, Fort Bend, Galveston,
Liberty, Montgomery, and Waller Counties, the executive director may allocate
up to 10% of the total HRVOC emissions allocated for those counties to all
such sites located in Brazoria, Chambers, Fort Bend, Galveston, Liberty, Montgomery,
and Waller Counties.
(3)
The executive director shall distribute all allowances
not allocated under this subsection proportionally to those sites receiving
allocations under subsections (a) and (b) of this section.
(d)
On March 31, 2006, the executive director will allocate
allowances to petroleum refineries as follows.
(1)
For petroleum refinery process units located in Harris
County, allowances for the emissions of one or more of the HRVOCs, will be
determined using the equation in the following figure.
(2) For petroleum refinery process units located in Brazoria,
Chambers, Fort Bend, Galveston, Liberty, Montgomery, and Waller Counties,
allowances for emissions of ethylene and propylene for each refinery will
be determined using the equation in the following figure.
(e) If the total actual HRVOC emissions from the covered facilities
at a site during a control period exceed the amount of allowances in the compliance
account for the site on March 1 following the control period, allowances for
the next control period shall be reduced by an amount equal to the emissions
exceeding the allowances in the compliance account plus 10% of the exceedance.
This allocation reduction does not preclude the executive director from initiating
an enforcement action. If a compliance account does not have sufficient allowances
to accommodate the reduction, it is the responsibility of the owner or operator
to purchase or transfer additional allowances within 30 days of the notice
of deficiency from the executive director.
(f)
Allowances will be allocated by the executive director,
who will deposit allowances into each compliance account:
(1)
initially, by March 31, 2006; and
(2)
subsequently, by January 1 of each following year.
(g)
The executive director may adjust the deposits for any
control period to reflect new or existing state implementation plan requirements.
(h)
The executive director may add or deduct allowances from
compliance accounts based on the review of reports required under §101.400
of this title (relating to Reporting).
(i)
To account for extenuating circumstances, the owner or
operator of a site may request that the executive director approve a substitution
as follows. In calculating the average level of activity, the level of activity
from one calendar year may be replaced with the level of activity from the
preceding or following calendar year. Applications for extenuating circumstances
shall be submitted by the owner or operator of the site to the executive director
no later than April 30, 2005. The executive director shall consider the following
circumstances as candidates for extenuating circumstances: production loss
due to Acts of God, fire, power outages, or other circumstances not attributable
to economic fluctuation.
(j)
Allocations for the first control period, April 1, 2006
through December 31, 2006, shall be reduced by 25% from the total annual allocation.
§101.396.Allowance Deductions.
(a)
On March 31 of each year after a control period, allowances
representing the total highly-reactive volatile organic compounds (HRVOC)
emissions from the covered facilities at a site during the previous control
period will be deducted from the compliance account for the site. The amount
of HRVOC emissions will be based upon the monitoring and testing protocols
established in §115.725 and §115.764 of this title (relating to
Monitoring and Testing Requirements), as appropriate.
(b)
The amount of HRVOC emissions from covered facilities shall
be calculated for each hour of the year and summed to determine the annual
emissions for compliance. For emissions from emissions events subject to the
requirements of §101.201 of this title (relating to Emissions Event Reporting
and Recordkeeping Requirements) or emissions from scheduled maintenance, startup,
or shutdown activities subject to the requirements of §101.211 of this
title (relating to Scheduled Maintenance, Startup, and Shutdown Reporting
and Recordkeeping Requirements); the hourly emissions to be included in the
summation shall not exceed the short-term limit of §115.722(c) and §115.761(c)
of this title (relating to Site-wide Cap and Control Requirements; and Site-wide
Cap).
(c)
If the monitoring and testing data referenced in subsection
(a) of this section does not exist or is unavailable, the site may determine
its HRVOC emissions for that period of time using the following methods and
in the following order: continuous monitoring data; periodic monitoring data;
testing data; data from manufacturers; and engineering calculations. When
determining the amount of HRVOC emissions under this subsection, the site
shall include a justification for using the substitute method or methods in
lieu of the methods referenced in subsection (a) of this section.
(d)
When deducting allowances from the compliance account of
a site for a control period, the executive director will deduct the allowances
beginning with the most recently allocated allowances before deducting banked
allowances.
§101.399.Allowance Banking and Trading.
(a)
Allowances allocated for a control period that are not
used for compliance in that control period may be banked for use in demonstrating
compliance for the next control period or transferred.
(b)
Allowances that have not expired or been used may be transferred
at any time during a control period, except as provided in this section.
(1)
The person desiring to transfer the allowances shall apply
for approval of the transaction to the executive director by submitting a
completed Form ECT-2, Application for Transfer of Allowances.
(2)
The ECT-2 form must include the purchase price per allowance
proposed to be paid, except for transactions between sites under common ownership
or control.
(3)
All information regarding the quantity and purchase price
of the allowances will be immediately made available to the public.
(4)
If the executive director approves the application, the
executive director will send a letter to the seller and purchaser reflecting
the transaction. The transaction is final upon issuance of the letter.
(c)
A person receiving allowances on an annual basis may permanently
transfer ownership of current and future allowances to any person in accordance
with the following requirements.
(1)
The person desiring to transfer the allowances shall apply
for approval of the transaction to the executive director by submitting a
completed Form ECT-4, Application for Permanent Transfer of Allowance Ownership.
(2)
The ECT-4 form must include the purchase price per allowance
proposed to be paid, except for transactions between sites under common ownership
or control.
(3)
All information regarding the quantity and purchase price
of the allowances will be immediately made available to the public.
(4)
If the executive director approves the application, the
executive director will send a letter to the seller and purchaser reflecting
the transaction. The transaction is final upon issuance of the letter.
(d)
A person may transfer allowances that are scheduled to
be allocated in a future control period but have not yet been deposited into
an account.
(1)
The person desiring to transfer the allowances shall apply
for approval of the transaction to the executive director by submitting a
completed Form ECT-5, Application for Transfer of Individual Future Year Allowances.
(2)
The ECT-5 form must include the purchase price per allowance
proposed to be paid, except for transactions between sites under common ownership
or control.
(3)
All information regarding the quantity and purchase price
of the allowances will be immediately made available to the public.
(4)
If the executive director approves the application, the
executive director will send a letter to the seller and purchaser reflecting
the transaction. The transaction is final upon issuance of the letter.
(e)
Allowances generated from sites located in counties other
than Harris County may not be used at sites located in Harris County. Allowances
generated from sites located in Harris County may not be used at sites located
in counties other than Harris County.
(f)
Only authorized account representatives may transfer allowances.
(g)
Allowances subject to an approved transaction will be deposited
into the purchaser's broker or compliance account within 30 days of receipt
of a completed transfer application.
§101.400.Reporting.
(a)
No later than March 31 after each control period, each
site shall submit a completed highly-reactive volatile organic compound (HRVOC)
Emissions Cap and Trade Annual Compliance Report to the executive director,
which shall include the following:
(1)
the total amount of actual HRVOC emissions from covered
facilities at the site during the preceding control period;
(2)
the method or methods used to determine the actual HRVOC
emissions, including, but not limited to, monitoring protocol and results,
calculation methodologies, and emission factors; and
(3)
a summary of all final transactions for the preceding control
period.
(b)
For sites failing to submit a HRVOC Emissions Cap and Trade
Annual Compliance Report by the required deadline in subsection (a) of this
section, the executive director may withhold approval of any proposed trades
from that site involving allowances allocated for the control period for which
the ECT-1 Form is due or to be allocated in subsequent control periods.
§101.401.Level of Activity Certification.
(a)
No later than April 30, 2005, the owner or operator of
each site subject to this division shall submit to the executive director
a completed Level of Activity Certification Form.
(b)
For each process unit subject to this division, the owner
or operator shall certify in the Level of Activity Certification Form the
level of activity for the five consecutive calendar year period of 2000 through
2004.
(c)
The owner or operator shall attach to the Level of Activity
Certification Form information and documentation necessary to support the
proposed level of activity baseline.
(d)
The owner or operator of the site may mark any portion
of the Level of Activity Certification Form, or supporting information and
documentation, relating to production and use of highly-reactive volatile
organic compounds, as confidential under Texas Health and Safety Code, §382.041.
§101.403.Program Audits and Reports.
(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.
(1)
The audit will evaluate the impact of the program on the
state's ozone attainment demonstration, the availability and cost of allowances,
compliance by the participants, and any other elements the executive director
may choose to include.
(2)
The executive director will recommend measures to remedy
any problems identified in the audit. The trading of allowances may be limited
or discontinued by the executive director in part or in whole and in any manner,
with commission approval, as a remedy for problems identified in the program
audit.
(3)
The audit data and results will be completed and submitted
to the United States Environmental Protection Agency and made available for
public inspection within six months after the audit begins.
(b)
No later than June 30, following the end of each control
period, the executive director shall develop and make available to the general
public and the United States Environmental Protection Agency, a report that
includes:
(1)
number of allowances allocated to each compliance account;
(2)
total number of allowances allocated under this division;
(3)
number of actual highly-reactive volatile organic compound
allowances subtracted from each compliance account based on the actual highly-reactive
volatile organic compound emissions from the site; and
(4)
a summary of all trades completed under 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 June 25, 2004.
TRD-200404252
Stephanie Bergeron
Director, Environmental Law Division
Texas Commission on Environmental Law Division
Earliest possible date of adoption: August 8, 2004
For further information, please call: (512) 239-4712
The Texas Commission on Environmental Quality (commission) proposes
amendments to §§115.10, 115.720, 115.722, 115.725 - 115.727, 115.729,
115.760, 115.761, 115.764, 115.769, 115.780 - 115.783, and 115.786 - 115.789.
The commission also proposes to repeal §§115.766 - 115.768 and 115.785,
and proposes new §115.766 and §115.767. These amendments, repeals,
and new sections are being proposed in Subchapter A, Definitions; Subchapter
H, Highly-Reactive Volatile Organic Compounds, Division 1, Vent Gas Control;
Subchapter H, Division 2, Cooling Tower Heat Exchange Systems; and Subchapter
H, Division 3, Fugitive Emissions.
The amended, repealed, and new sections are proposed to be submitted to
the United States Environmental Protection Agency (EPA) as revisions to the
state implementation plan (SIP).
BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES
The Houston/Galveston/Brazoria ozone nonattainment area (HGA) is classified
as Severe-17 under the Federal Clean Air Act Amendments of 1990 (as codified
in 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 (125 parts per billion) by November 15, 2007. The
HGA consists of Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty,
Montgomery, and Waller Counties, and the commission has been working to develop
a demonstration of attainment in accordance with 42 USC, §7410. The most
relevant HGA SIP revisions to date are the December 2000 one-hour ozone standard
attainment demonstration, the September 2001 follow-up revision, and the December
2002 nitrogen oxides (NO
x
)/highly-reactive volatile
organic compound (HRVOC) revision.
This process has proven to be extremely challenging due to the magnitude
of reductions needed for attainment. The emission reduction requirements included
as part of the December 2000 SIP revision represent substantial, intensive
efforts on the part of stakeholder coalitions in the HGA, in partnership with
the commission, to address ozone. These coalitions include local governmental
entities, elected officials, environmental groups, industry, consultants,
and the public, as well as EPA and the commission, and worked diligently to
identify and quantify control strategy measures for the HGA attainment demonstration.
December 2000
The December 2000 SIP revision contained rules and photochemical modeling
analyses in support of the HGA ozone attainment demonstration. The majority
of the emissions reductions identified in this revision were from a 90% reduction
in point source NO
x
. The modeling analysis also
indicated a shortfall in necessary NO
x
emission
reductions, such that an additional 91 tons per day (tpd) of NO
x
reductions were necessary for an approvable attainment demonstration.
In addition, the revision contained post-1999 rate-of-progress (ROP) plans
for the milestone years 2002 and 2005 and for the attainment year 2007, and
transportation conformity motor vehicle emissions budgets (MVEB) for NO
September 2001
The September 2001 SIP revision for the HGA included the following elements:
1) corrections to the ROP table/budget for the years 2002, 2005, and 2007
due to a mathematical inconsistency; 2) incorporation of a change to the idling
restriction control strategy to clarify that the operator of a rented or leased
vehicle is responsible for compliance with the requirements in situations
where the operator of a leased or rented vehicle is not employed by the owner
of the vehicle (the commission committed to making this change when the rule
was adopted in December 2000); 3) incorporation of revisions to the clean
diesel fuel rules to provide greater flexibility for compliance with the requirements
of the rule while preserving the emission reductions necessary to demonstrate
attainment in the HGA; 4) incorporation of a stationary diesel engine rule
that was developed as a result of the state's analysis of EPA's reasonably
available control measures; 5) incorporation of revisions to the point source
NO
x
rules; 6) incorporation of revisions to the
emissions cap and trade rules; 7) the removal of the construction equipment
operating restriction and the accelerated purchase requirement for Tier 2/3
heavy-duty equipment; 8) the replacement of these rules with the Texas Emission
Reduction Plan program; 9) the layout of the midcourse review process that
details how the state will fulfill the commitment to obtain the additional
emission reductions necessary to demonstrate attainment of the one-hour ozone
standard in the HGA; and 10) replacement of the 2007 ROP MVEBs to be consistent
with the attainment MVEBs.
As was discussed in the December 2000 revision, the modeling resulted in
a 141 parts per billion peak ozone level that correlated to a shortfall calculation
of 91 tpd NO
x
equivalent emissions. An additional
five tpd was added to the shortfall, because the state could not take credit
for the NO
x
reductions associated with the diesel
pull-ahead strategy. The excess emissions from this strategy were not included
in the original emissions inventory. The gap control measures adopted in December
2000, along with the stationary diesel engine rules included in the September
2001 revision, resulted in NO
x
reductions of
40 tpd, which left a total remaining shortfall of 56 tpd. The state committed
to address this shortfall through the midcourse review process.
December 2002
In January 2001, the Business Coalition for Clean Air--Appeal Group (BCCA-AG)
and several regulated companies challenged the December 2000 HGA SIP and some
of the associated rules. Specifically, the BCCA-AG challenged the 90% NO
In compliance with the consent order, the commission conducted a scientific
evaluation based in large part on aircraft data collected by the Texas 2000
Air Quality Study (TexAQS). The TexAQS, a comprehensive research project conducted
in August and September 2000 involving more than 40 research organizations
and over 200 scientists, studied ground-level ozone air pollution in the HGA
and East Texas regions. The study revealed that while industrial source NO
To address these findings and to fulfill obligations in the consent order,
the commission adopted a SIP revision in December 2002 that focused on replacing
the most stringent 10% industrial NO
x
reductions
with VOC controls. In light of the TexAQS study, the commission conducted
further modeling analysis of ambient VOC data. The results of photochemical
grid modeling and analysis indicated that the same level of air quality benefits
achieved with a 90% industrial NO
x
emissions
reduction could be achieved with an overall 80% industrial NO
x
emissions reduction when combined with an industrial VOC emissions
reduction. This conclusion was based on results from several studies, including
photochemical grid modeling of the August-September 2000 episode using a top-down
emissions inventory adjustment to point source HRVOC emissions, and analyses
of ambient HRVOC measurements made by commission automated gas chromatographs
and airborne canisters using the maximum incremental reactivity and hydroxyl
reactivity scales. Four HRVOCs (ethylene, propylene, 1,3-butadiene, and butenes)
clearly play important roles in the HGA ozone formation, and these four seemed
to be the best candidates for the first round of HRVOC controls.
In order to address these scientific findings, the commission adopted revisions
to the industrial source control requirements, one of the control strategies
within the existing federally approved SIP. The December 2002 revision contains
new rules to reduce HRVOC emissions from four key industrial sources: fugitives,
flares, process vents, and cooling towers. The adopted rules target HRVOCs
while maintaining the integrity of the SIP. Analysis showed that limiting
emissions of ethylene, propylene, 1,3-butadiene, and butenes in conjunction
with an 80% reduction in NO
x
is equivalent in
terms of air quality benefit to that resulting from a 90% point source NO
The technical support documentation accompanying the revision contains
the supporting analysis for early results from ongoing analysis examining
whether reductions in HRVOC emissions could replace the last 10% of industrial
NO
x
controls with a reduction of approximately
64% in industrial HRVOC emissions, while ensuring that the air quality specified
in the approved December 2000 HGA SIP is met.
Current SIP Revision
As mentioned previously, the commission committed to perform a midcourse
review to ensure attainment of the one-hour ozone standard. The midcourse
review process provides the ability to update emissions inventory data, utilize
current modeling tools, such as MOBILE6, and enhance the photochemical grid
modeling. The data gathered from the TexAQS continues to improve photochemical
modeling of the HGA. The collection of these technical improvements give a
more comprehensive understanding of the ozone challenge in the HGA that is
necessary to develop an attainment plan. In the early part of 2003, the commission
was preparing to move forward with the midcourse review; however, during the
same time period EPA announced its plans to begin implementation of the eight-hour
ozone standard. The EPA published proposed rules for implementation of the
eight-hour ozone standard in the June 2, 2003 issue of the
Federal Register
(68 FR 32802). In the same time frame, EPA also formalized
its intentions to designate areas for the eight-hour ozone standard by April
15, 2004, meaning states would need to reassess their efforts and control
strategies to address this new standard by 2007. Recognizing that existing
one-hour nonattainment areas would soon be subject to the eight-hour ozone
standard, and in an effort to efficiently manage the state's limited resources,
the commission decided to develop an approach that addresses the outstanding
obligations under the one-hour ozone standard while beginning to analyze eight-hour
ozone issues.
The commission's one-hour ozone SIP commitments include: 1) completing
a one-hour ozone midcourse review; 2) performing modeling; 3) adopting measures
sufficient to fill the NO
x
shortfall; 4) adopting
measures sufficient to demonstrate attainment; and 5) revising the MVEB using
MOBILE6.
Results from the TexAQS and recent photochemical modeling indicate that
additional HRVOC reductions will be the most beneficial measure to reduce
ozone in the HGA. The commission is proposing to reduce HRVOC emissions to
reach attainment of the one-hour ozone standard. The photochemical modeling
of the August-September 2000 episode coupled with a weight-of-evidence argument
demonstrates attainment of the one-hour ozone standard. To achieve the necessary
HRVOC reductions, the commission is proposing a two-pronged approach that
would address variable short-term emissions through a not-to-exceed limit,
and would address steady-state and routine emissions through an annual cap.
The annual HRVOC cap in Harris County would be reduced from the existing HRVOC
cap in order to support the attainment demonstration modeling. The annual
HRVOC cap in the seven-county surrounding area is equivalent to the total
emissions limits established in the December 2002 SIP revision, but represented
on an annual basis instead of a 24-hour rolling average. The commission will
continue to evaluate the necessity to require short-term and annual reductions
from those sites subject to Chapter 115, Subchapter H, Divisions 1 and 2,
that are located within the seven-county surrounding area. If the evaluation
demonstrates that reductions from these counties have little impact on attainment
of the one-hour ozone standard, the short-term and annual limits for those
other seven counties may no longer be required. The commission also solicits
comments on possible ways to mitigate violations of the short-term emissions
cap.
The annual HRVOC cap emissions would be distributed and enforced through
an HRVOC emissions cap and trade program under 30 TAC Chapter 101, Subchapter
H, new Division 6 (Highly-Reactive Volatile Organic Compound Emissions Cap
and Trade Program) being proposed in concurrent rulemaking. This program would
establish a mandatory annual HRVOC emissions cap on all sites located in the
HGA that emit or have the potential to emit more than ten tons per year of
HRVOC, and that are subject to the HRVOC control requirements of Chapter 115,
Subchapter H, Division 1 or Division 2. The cap would be enforced by the allocation,
trading, and banking of allowances. An allowance is the equivalent of one
ton of HRVOC emissions. This HRVOC cap would be established at levels demonstrated
as necessary to allow the HGA to attain the one-hour ozone standard. The proposed
cap would initially be implemented on April 1, 2006. The proposed HRVOC cap
and trade program would also require all sites with new or modified HRVOC
sources in the HGA to obtain unused allowances from other sites already participating
under the cap to offset any increased HRVOC emissions. For sites that have
the potential to emit ten tons per year or less of HRVOCs from sources subject
to the HRVOC control requirements of Subchapter H, Division 1 or 2, the total
aggregate HRVOC emissions from those sources would be limited to ten tons
per year. Sites that are exempt from the HRVOC emissions cap and trade program
would be extended an opportunity to opt-in, receive an HRVOC allocation, and
thereby not be restricted to the ten tons per year limit.
The HGA SIP no longer relies solely on NO
x
-based
strategies. A combination of point source HRVOC controls and NO
x
reductions appear to be the most effective means of reducing ozone
in the HGA and there is no longer a NO
x
shortfall
in the HGA SIP. The commission also evaluated a number of the existing control
strategies that were put in place in the December 2000 revision. The photochemical
modeling shows that some of these strategies are no longer necessary to attain
the one-hour ozone standard. This SIP revision is proposing the repeal of
the commercial lawn and garden equipment restrictions, the repeal of the heavy-duty
vehicle idling restrictions, and the removal of the motor vehicle inspection
and maintenance program requirements from Chambers, Liberty, and Waller Counties.
In addition, this SIP proposal includes revisions to the environmental speed
limit strategy. In September 2002, the commission revised the existing speed
limit strategy to suspend the 55 mile per hour (mph) speed limit until May
1, 2005, and, where posted speeds were 65 mph or higher before May 1, 2002,
to increase speed limits to five mph below what was posted. The 78th Legislature,
2003, removed the commission's authority to determine speed limits for environmental
purposes; therefore, this proposal would remove the reinstatement of the 55
mph speed limit on May 1, 2005, and would maintain the currently posted speed
limits at five mph below the posted limit before May 1, 2002. Also, as part
of this SIP revision, the commission is proposing new statewide portable fuel
container rules. Historically, the commission has expressed a preference to
implement technology-based strategies over behavior-altering strategies, and
these proposed changes embody that philosophy.
Through this revision, the commission is fulfilling its outstanding one-hour
ozone SIP obligations and beginning to plan for the upcoming eight-hour ozone
standard. This proposal demonstrates attainment of the one-hour ozone standard
in the HGA in 2007 and provides a preliminary analysis of the HGA in terms
of the eight-hour ozone standard in 2007 and 2010. EPA's proposed eight-hour
implementation rules provide flexibility to the states in transitioning from
the one-hour to the eight-hour ozone standard, and the commission believes
the steps taken in this proposal and the technical work performed to date
will be invaluable through the transition period. Upon EPA's finalization
of the eight-hour implementation and the transportation conformity rules,
the commission expects to begin developing eight-hour ozone SIPs.
This is to put all interested parties on notice that, although the commission
is proposing the following rules, including an annual cap and a short-term
limit on HRVOC emissions, the commission may significantly amend these proposed
rules at adoption, repropose a portion of these rules, or propose additional
rules, as appropriate.
First, the commission continues to analyze the rules for implementation
of the eight-hour ozone standard adopted by EPA on April 15, 2004. These rules
and their preamble suggest that a demonstration of attainment of the one-hour
ozone standard may not be required for the portion of the SIP pertaining to
the HGA. This means that the commission will need to review the measures contained
in the current proposal to ensure that they are needed in this form in order
to demonstrate noninterference. Additional analysis of the impact of the proposed
rules on attainment of the eight-hour standard may indicate a need for new
or more stringent control measures.
Second, the commission may determine that, if a one-hour attainment demonstration
is necessary, additional, different, or more stringent control measures may
be needed based on additional modeling. The commission staff continues to
model scenarios under the one-hour standard, and the commission may determine
that the results indicate a need for changes in control strategies. Moreover,
the one-hour attainment demonstration includes a weight-of-evidence argument.
Additional review of the issues relating to the weight-of-evidence argument
could lead the commission to propose new strategies or to repropose the control
strategies proposed today.
Finally, the commission is also concurrently proposing a cap and trade
program in Chapter 101, Subchapter H, new Division 6 as a refinement of the
annual cap proposed for HRVOC emissions.
SECTION BY SECTION DISCUSSION
General Administrative Rule Language Changes
The commission proposes to change the word "which" to "that" and the word
"shall" to "must" in numerous locations in the rule language to conform to
the drafting rules in the
Texas Legislative Council
Drafting Manual
, October 2002.
The commission proposes to spell out acronyms the first time they are used
in a section and to delete acronyms that are only used once in a section.
SUBCHAPTER A, DEFINITIONS
The proposed amendment to §115.10, concerning Definitions, would add
a new definition of "Emergency flare" to differentiate flares that only receive
emissions during upset events or unscheduled maintenance, startup, or shutdown
activities from other flares. The remaining definitions in §115.10 are
proposed to be renumbered accordingly.
The proposed amendment to the definition of "Strippable volatile organic
compound" would remove the listing of test methods used to determine the concentration
of strippable VOC because the test methods are not necessary to define the
term and are already listed in the cooling tower rules.
SUBCHAPTER H, HIGHLY-REACTIVE VOLATILE ORGANIC
COMPOUNDS
Division 1, Vent Gas Control
Section 115.720, Applicability and Definitions
The proposed amendment to §115.720(a) would add language to specify
that the applicability of this rule includes both controlled and uncontrolled
vent gas streams containing HRVOC. A new definition for "Degassing safety
device" is proposed in §115.720(b) to address low-flow pilots that are
typically permitted as flares, but used only at geologic storage facilities
during emergency releases. The remaining definitions in §115.720 are
proposed to be renumbered accordingly.
Section 115.722, Site-wide Cap and Control Requirements
The commission proposes to amend this section to allow sites the flexibility
of compliance with the vent gas control requirements of this division through
compliance with the HRVOC emissions cap and trade program. The proposed amendment
to §115.722(a) would change the long-term site-wide cap strategy to a
calendar year basis instead of the existing 24-hour rolling average basis,
and would state that owners or operators of a site subject to the HRVOC vent
gas rules shall comply with the HRVOC emissions cap and trade program in Chapter
101, Subchapter H, Division 6. The proposed amendment to §115.722(a)
would also remove the reference to the site-cap limits in the tables of the
SIP.
Proposed new §115.722(b) would specify that all sites subject to this
division or to Division 2 that are exempt from the HRVOC emissions cap and
trade program in accordance with §101.392 (Exemptions) are limited to
ten tons of HRVOC emissions per calendar year.
Proposed new §115.722(c) would provide a short-term, not-to-exceed
limit, in pounds of HRVOC per one-hour block, for all sites subject to this
division. The commission continues to evaluate the magnitude of the short-term
limit, and the time period over which this short-term limit would be enforced.
The commission solicits comment regarding the appropriate level for this short-term
limit, and requests any supporting data regarding alternatives to the magnitude
and time period. Proposed new §115.722(c)(3) would address how exceedances
of the short-term limits should be calculated to determine compliance with
the long-term cap. Existing §115.722(b) and (c) are proposed to be relettered
to §115.722(d) and (e), respectively. The proposed amendment to relettered §115.722(d)
would correct a citation to 40 Code of Federal Regulations (CFR) §60.18
and add two new paragraphs to specify the methods to demonstrate compliance
with the minimum net heating value requirements and the maximum exit velocity
requirements. The commission does not propose to require continuous monitoring
of potential visible emissions from flares.
Section 115.725, Monitoring and Testing Requirements
The proposed amendment to §115.725(a) would specify that pressure
relief valves are not subject to the requirements of §115.725(a). Proposed §115.725(a)
would also specify that each vent gas that is not controlled by a flare must
be tested. The proposed amendment to §115.725(a) would specify that HRVOC
emissions are considered to be zero during non-operational periods for cyclic
or batch processes. Additionally, the proposed amendment to §115.725(a)
would add requirements in §115.725(a)(1) and (2) for owners or operators
to select operational parameters for uncontrolled and controlled vents, monitor
those parameters, and establish operating limits based on averages during
the tests required by §115.725(a). The process parameter monitoring requirements
are necessary to help assure compliance with the site-wide caps in §115.722(c).
Proposed new §115.725(a)(3) would require that HRVOC emissions during
emissions events and scheduled startup, shutdown, and maintenance activities
be determined using either testing or process knowledge and engineering calculations.
This requirement is necessary due to the inclusion of emissions from emissions
events and scheduled startup, shutdown, and maintenance activities in the
site-wide caps in §115.722 and to better assure compliance with the HGA
attainment demonstration SIP. Proposed new §115.725(a)(4) would require
the owner or operator to develop, implement, and follow written monitoring
plans for the operational parameters required under §115.725(a)(1) and
(2). Proposed new §115.725(a)(5) would specify that additional testing
may be performed to update emission data after the initial HRVOC emission
test has been performed, and that test plans for additional testing must be
submitted to the executive director at least 45 days prior to testing. Proposed
new §115.725(a)(6) would include the provisions currently under §115.725(c),
regarding the use of testing performed prior to approval of the test plans,
and proposed new §115.725(a)(7) would include the language currently
under §115.725(g), regarding test waivers for one-half of the vents that
are identical in design and operation.
The proposed amendment to §115.725(b) would specify that the alternatives
provided may not be applied to pressure relief valves and that the vent gas
stream must comply with the process parameter monitoring requirements of §115.725(a).
The proposed amendment to §115.725(b)(1)(B) would specify that cylinder
gas audits must be performed at a minimum quarterly, after the initial cylinder
gas audit. The proposed amendment in §115.725(b)(2) would specify that
process data, "sufficient to demonstrate compliance status" may be used to
determine maximum potential HRVOC hourly emissions, and would remove pressure
relief valves from the types of processes for which process knowledge may
be used. Finally, the proposed amendment to §115.725(b) would include
the addition of degassing safety devices in §115.725(b)(2)(D) to the
types of processes for which process knowledge may be used in lieu of testing.
Proposed new §115.725(c) would provide monitoring requirements for
pressure relief valves, and the proposed new language in §115.725(c)(1)
would specify the requirements of the pressure relief valve monitoring system.
Proposed new §115.725(c)(2) would specify that the owner or operator
may use process knowledge to determine the HRVOC emission rates during events
when the pressure relief valves open. Proposed new §115.725(c)(3) would
require written monitoring plans for the pressure relief valve monitoring
systems, and would specify the requirements of the plans. Finally, proposed
new §115.725(c)(4) would specify that the written monitoring plans must
be submitted within 30 days upon written request by the executive director,
and that the executive director may require additional or alternative monitoring
requirements.
The proposed amendment to §115.725(d) would specify that except for
subsections (e) - (i), the owner or operator shall perform continuous monitoring
in accordance with the requirements of §115.725(d) to demonstrate compliance
with §115.722(a) - (d). The proposed amendment to §115.725(d)(2)
would revise the calibration requirements for the on-line analyzer. The proposed
amendment to §115.725(d)(2)(A)(i) would specify that for HRVOC constituents,
the owner or operator must follow the procedures and requirements of 40 CFR
Part 60, Appendix B, Section 10 of Performance Specification 9, except as
provided for in §115.725(d)(2)(A)(i). Proposed new §115.725(d)(2)(A)(ii)
would specify that for the constituents monitoring to determine net heating
value and molecular weight, the owner or operator may elect to follow the §115.725(d)(2)(A)(i)
calibration requirements or the manufacturer recommended procedures. Proposed
new §115.725(d)(2)(A)(ii)(I) would require that if the manufacturer recommended
procedures are selected, those procedures must include, at a minimum, weekly
calibration checks of the top two non-HRVOC constituents affecting molecular
weight and net heating value to meet the performance criteria of Section 10.2
of Performance Specification 9. Proposed new §115.725(d)(2)(A)(ii)(II)
would require that manufacturer information and data be submitted with a quality
assurance plan (QAP) for those constituents for which routine calibration
is not performed. Proposed new §115.725(d)(2)(A)(iii) would specify that
the range of calibration standards required for calibration of the on-line
analyzer may be based on the typical concentrations instead of the full potential
range of concentrations. The language in §115.725(d)(2)(A)(iii) would
also specify that data must be submitted with the QAP to demonstrate the accuracy
of the analyzer at the maximum concentrations outside the proposed calibration
range. Proposed new §115.725(d)(2)(A)(iv) would state that the executive
director may specify calibration requirements in the approval of the QAP.
Finally, proposed new §115.725(d)(2)(B) would specify that the owner
or operator may install an on-line calorimeter to determine net heating value
instead of monitoring for individual constituents to determine net heating
value. It has come to the commission's attention that a reference in Performance
Specification 9, Section 10.1 correctly cites Section 13.3 of Performance
Specification 9 with regard to the acceptance criteria for multipoint calibration
requirements. Section 13.3 would require industry to comply with a five-minute
sampling frequency for the on-line analyzers. The correct citation for the
precision and linearity requirements should be Section 13.2 of Performance
Specification 9. The commission has confirmed the appropriate citation with
the EPA. Therefore, it is the commission's position that industry should comply
with the multipoint calibration requirements in Section 13.2 of Performance
Specification 9.
The proposed amendment to §115.725(d)(3) would specify the calculation
methodology for determining the percent measurement data availability. The
proposed amendment to §115.725(d)(4) would change the start of daily
sampling from within 24 hours to within ten hours of initial on-line analyzer
malfunction, and would specify that the samples collected during periods of
monitor downtime shall be used to demonstrate "continuous compliance with
the requirements of §115.722(a) - (d) of this title." The proposed amendment
to §115.725(d)(5) would delete the move the language specifying that
compliance with the minimum net heating value requirements is based on block
one-hour average to §115.722(d)(1). The language currently in §115.725(d)(7)
would be renumbered to §115.725(d)(6) and revised to move language to §115.722(d)(2)
specifying that compliance with the exit velocity requirements is based on
a block one-hour average. Additionally, §115.725(d)(6) would be renumbered
to §115.725(d)(7) and revised to specify that HRVOC emission rates shall
be calculated from data gathered according to paragraphs (1) - (6), and to
specify that the heating value requirement is based on net heating value.
Finally, in order to better organize the monitoring and testing rules, §115.725(d)(8)
regarding minor modifications to the methods and alternative monitoring methods,
is proposed to be moved to a new §115.725(j) and the language revised
to better specify the requirements.
Section 115.725(e) currently states that flares used solely for abatement
of emissions from loading operations for transport vessels or temporary portable
flares used solely for the abatement of emissions from scheduled maintenance
or startup or shutdown activities are not required to comply with the monitoring
requirement of §115.725(d) provided specific requirements are satisfied.
The proposed amendment to §115.725(e) specifies that this subsection
would only apply to flares used solely for abatement of HRVOC emissions, would
apply to loading operations from marine vessels, and would not apply to temporary
portable flares used solely for scheduled startup, shutdown, or maintenance
activities. The proposed amendment to §115.725(e) would also move the
recordkeeping requirements in §115.725(e)(1)(B) to §115.726(d)(5),
and renumber §115.725(e)(1)(A) - (D) to §115.725(e)(1) - (3). The
proposed amendment to §115.725(e)(1) - (3) would also specify the requirements
to demonstrate compliance with the minimum net heating value requirements
and the exit velocity requirements of §115.722(d), and compliance with
the site-wide cap in §115.722. Proposed new §115.725(e)(4) would
specify that the owner or operator may use process knowledge to determine
net heating value and HRVOC emissions for flares that receive greater than
98% of an individual HRVOC at all times.
The proposed amendment would reletter §115.725(f) to §115.725(j)
and specify that minor modifications to either test methods or monitoring
methods may be approved by the executive director.
Proposed new §115.725(f) would specify monitoring requirements for
flares used solely for abatement of emissions from scheduled startup, shutdown,
and maintenance activities. Proposed new §115.725(f) would incorporate
language removed from §115.725(e)(2), regarding temporary portable flares;
however, but would also expand the applicability to any flare type used solely
for scheduled startup, shutdown, and maintenance activities. Proposed new §115.725(f)(2)
would limit the total number of days to 28 days in 12 consecutive months for
which an account may temporarily send HRVOC to multiple flares under the provisions
of §115.725(f). Proposed new §115.725(f)(6) would specify that the
owner or operator may use process knowledge to determine net heating value
and HRVOC emissions for flares that receive greater than 98% of an individual
HRVOC at all times.
The proposed amendment to §115.725(g), regarding test waivers for
one-half of the vents that are identical in design and operation, would move
the language to §115.725(a)(8).
Proposed new §115.725(g) would specify monitoring requirements for
emergency flares as proposed to be defined in §115.10. Proposed new §115.725(g)(1)
and (2) would provide the option of complying with the monitoring requirements
of §115.725(d) or using process knowledge and engineering calculations
to determine compliance with §115.722(a) - (d). Proposed new §115.725(g)(2)
would specify additional requirements for emergency flares for which process
knowledge and engineering calculations are used. Proposed new §115.725(g)(2)(A)
would specify parameter monitoring for emergency flares with physical seals,
such as water seals, to monitor the status of the physical seals, record the
time and duration of each event when emissions are sent to the flare, and
verifies that the seals have been restored after an event. Proposed new §115.725(g)(2)(B)
would specify parameter monitoring for emergency flares without physical seals
to monitor flow to the emergency flare with a flow monitor or flow indicator
to determine the time and duration of each event when emissions are sent to
the flare and to determine the minimum flow rate that indicates when emissions
are sent to the flare. Proposed new §115.725(g)(2)(C) would specify that
any owner or operator electing to use process knowledge for emergency flares,
must develop, implement, and follow a written monitoring plan for the parameter
monitoring under §115.725(g)(2)(A) or (B). Proposed new §115.725(g)(2)(D)
would specify that the written monitoring plans must be submitted within 30
days upon written request by the executive director. Proposed new §115.725(g)(2)(E)
would specify the calculation methods for the actual exit velocity and the
HRVOC hourly average mass emission rate from the flare, and the destruction
efficiencies for various situations.
Proposed new §115.725(h) would specify requirements for flares other
than emergency flares that temporarily receive HRVOC emissions from activities
other than scheduled startup, shutdown, and maintenance. Proposed new §115.725(h)(1)
and (2) would limit the total number of days that HRVOC may be temporarily
sent to an individual flare, or to multiple flares at an account under the
provisions of §115.725(h). Proposed new §115.725(h)(3) would options
to determine flow rate to the flare in lieu of monitoring in accordance with §115.725(d)(2),
including process knowledge, actual measurement, or for flares that temporarily
receive HRVOC emissions from flare systems that are monitored according to §115.725(d),
data substitution. Proposed new §115.725(h)(4) would specify options
to determine net heating value and HRVOC constituents in lieu of monitoring
in accordance with §115.725(d)(2), including daily sampling according
to §115.725(d)(4) or, for flares that temporarily receive HRVOC emissions
from flare systems that are monitored according §115.725(d), data substitution
for time periods up to 72 consecutive hours. Finally, proposed new §115.725(h)(5)
would specify that, if an emissions event occurs while HRVOC emissions are
sent temporarily to a flare under §115.725(h), then process knowledge
may be used to determine compliance with §115.722(a) - (d).
Proposed new §115.725(i) would specify that process knowledge may
be used to determine compliance with §115.722(a) - (d) for flares that
are specifically designed to receive and control liquid or dual phase streams.
This amendment is necessary because the monitoring provisions in the §115.725
are not applicable to flares designed to control liquid streams, and the current
state of monitoring technology is not sufficient to allow continuous monitoring
of dual phase streams.
Proposed new §115.725(j) (that was relettered from §115.725(f))
would incorporate language previously in §115.725(f) to specify that
minor modifications to either test methods or monitoring methods may be approved
the executive director.
Finally, proposed new §115.725(k) would specify that when process
information and engineering calculations are used to demonstrate compliance
with §115.722(a) - (d), the process information and engineering calculations
must be submitted within 30 days upon written request by the executive director.
This addition to §115.725 is necessary to ensure the commission has adequate
information to determine compliance with the site-wide caps.
Section 115.726, Recordkeeping and Reporting Requirements
The proposed amendment to §115.726(a) would remove the unnecessary
language specifying review of test plans and QAPs, and would specify that
the owner or operator of each affected flare or vent gas stream subject must
subsequently comply with the approved testing plans and QAPs for monitoring.
The proposed amendment to §115.726(a)(1) would specify that the paragraph
applies to the monitoring requirements in §115.725(d) and the proposed
amendment to §115.726(a)(1)(A) would specify the latest date that the
QAP must be submitted. The proposed amendment to §115.726(a)(1)(B) would
change the requirement to submit QAP for flares that become subject to the
requirements of the division after the compliance date. The proposed amendment
to §115.726(a)(1)(B) would change the requirement to submit the QAP at
least 60 days prior to the flare being place in HRVOC service by removing
the 60-day time period and only require that the QAP be submitted prior to
the flare being placed in HRVOC service. The proposed amendment to §115.726(a)(2)
would specify that the paragraph only applies to the testing requirements
in §115.725(a). Additionally, proposed new §115.726(a)(2)(D) would
specify that the operation parameters required in proposed new provisions
in §115.725(a)(1) and (2) must be identified in the test plan.
The proposed amendment to §115.726(b) would include more specific
recordkeeping requirements of the vent testing and monitoring conducted as
required by §115.725(a) and (b). Proposed new §115.726(b)(1) - (3)
would include the addition of recordkeeping requirements for the process parameter
monitoring and monitoring plans required under proposed new §115.725(a)(1),
(2), and (4). Additionally, proposed new §115.726(b)(4) - (7) would provide
more specific recordkeeping requirements for vent gas streams monitored using
a continuous emission monitoring systems in accordance with §115.725(b)(1),
and for vent gas streams for which alternatives to testing have been allowed
under §115.726(b)(2).
The proposed amendment would reletter §115.726(c), relating to recordkeeping
requirements for flares monitored in accordance with §115.725, to §115.726(d).
Proposed new §115.726(c) would include recordkeeping requirements for
affected pressure relief valves monitored in accordance with the proposed
new provisions in §115.725(c). The proposed additional recordkeeping
requirements would include records of the date, time, duration, volumetric
flow rate, and speciated and total HRVOC emissions for each pressure relief
event. The proposed recordkeeping requirements for affected pressure relief
valves would include records of the parameters monitored in accordance with §115.725(c)(1),
all process information, data, and calculations used to determine flow and
emission data as specified in §115.725(c)(2), and the monitoring plans
required under §115.725(c)(3).
The proposed amendment to §115.726(d) (that was relettered from §115.726(c))
would specify that the recordkeeping requirements are for flares monitored
in accordance with §115.725. The proposed amendment to §115.726(d)(4)
(that was renumbered from §115.726(c)(4)) would specify that the records
maintained for the calculated net heating values and exit velocities must
be recorded on a 15-minute average basis rather than instantaneous values.
Proposed new §115.726(d)(5) would specify recordkeeping requirements
specific to flares used solely for loading operations under §115.725(e),
in addition to the general flare recordkeeping requirements in §115.726(d)(1)
- (4). The proposed new language in §115.726(d)(5) would incorporate
recordkeeping requirements moved from §115.725(e)(1)(B) and the requirement
in §115.726(d)(5)(A) would require the size of vessel being loading instead
of the type of vessel.
Proposed new §115.726(d)(6) would specify recordkeeping requirements
specific to flares used solely for scheduled startup, shutdown, and maintenance
activities under §115.725(f), in addition to the general flare recordkeeping
requirements in §115.726(d)(1) - (4). Similarly, proposed new §115.726(d)(7)
would specify recordkeeping requirements specific to emergency flares subject
to §115.725(g), in addition to the general flare recordkeeping requirements
in §115.726(d)(1) - (4). Finally, proposed new §115.726(d)(8) would
specify recordkeeping requirements specific to flares subject to the requirements
of §115.725(h) or (i), in addition to the general flare recordkeeping
requirements in §115.726(d)(1) - (4).
The proposed amendment would reletter §115.726(d), related to records
for exemptions to §115.726(e), and would specify that the records correspond
to the exemptions listed in §115.727(a) - (e). The proposed amendment
to §115.726(e)(1) (that was renumbered from §115.726(d)(1)) would
specify that the records applied to vent gas streams that are routed to flares
and that contain less than 5.0% by weight HRVOC, and to vent gas streams that
are not routed to flares that does not exceed 100 parts per million by volume
HRVOC. The proposed amendment to §115.726(e)(3) would correct cross-references.
The proposed amendment would reletter §115.726(f) to §115.726(i)
and add a new §115.726(f) that would specify that an owner or operator
claiming exemption under §115.727(e) must submit written notification
at least 15 days prior to permanently removing a flare from service, but no
later than December 31, 2005.
The proposed amendment would reletter §115.726(e) to §115.726(g).
The proposed amendment to §115.726(g) would specify that daily records
are required to demonstrate compliance with the tons per calendar year emissions
limits in §115.722(a) and (b). Furthermore, the proposed amendment to §115.726(g)(2)
would include pressure relief valves in addition to all flares and vents subject
to §115.725. Finally, the proposed amendment would delete §115.726(g)(3)
because this specific recordkeeping requirement would be moved to §115.726(g)(2).
Proposed new §115.726(h) would specify the recordkeeping requirements
to demonstrate compliance with the one-hour block emission limits in §115.722(c).
The proposed amendment to §115.726(i) (relettered from §115.726(f))
would specify that records must be maintained on-site.
Section 115.727, Exemptions
The proposed amendment to §115.727(b)(1) and (2) would correct cross-references.
Additionally, the proposed amendment to §115.727 would delete §115.727(c)
that specified that emissions from scheduled maintenance, startup, and shutdown
activities in compliance with 30 TAC §101.211 are exempt from the requirements
of §115.722(a), and §115.727(d) that specifies that emissions from
emissions events in compliance with §101.201 are exempt from the requirements
of §115.722(a). The proposal to remove the exemptions in §115.727(c)
and (d) is necessary to better ensure an approvable SIP and the demonstration
of attainment.
The proposed amendment would reletter §115.727(e) to §115.727(c)
and include the addition of language to specify that the exemptions in §115.727(c)
may apply to vent gas streams that are not routed to a flare. The proposed
amendment to §115.727(c)(1) - (3) would correct cross-references. The
proposed amendment to §115.727(c)(2) would also add language to provide
exemption for vent gas streams with low volumetric rates equal to or less
than 100 dry standard cubic feet per hour. This proposed revision provides
flexibility for exempting vent gas streams that may exceed the 100 parts per
million by volume exemption level already provided, but have minimal HRVOC
emissions due to very low volumetric flow rate. An additional proposed amendment
to §115.727(c)(2) would specify that the 5.0% limit for the total number
of vents claimed exempt under §115.727(c)(2) is based on the long-term
pound per hour cap limitation in §115.722(a) or (b). Finally, the proposed
amendment to §115.727(c)(3)(A) would add incinerators to list of the
sources for which an exemption may be claimed and would specify that the exemption
for vent gas streams resulting from the combustion of less than 5.0% HRVOC
is "by weight."
The proposed amendment would reletter §115.727(f) to §115.727(d)
and correct a cross-reference.
Proposed new §115.727(e) would specify that any flares that will be
permanently out of service by April 1, 2006 are exempt from the requirements
of the division except for the recordkeeping requirements of §115.726(f).
The new proposed exemption will provide relief for owner or operators with
flares that will be permanently taken out of service after the December 31,
2005 compliance date to install continuous monitoring equipment, but prior
to the April 1, 2006 compliance date for the site-wide caps in §115.722.
Section 115.729, Counties and Compliance Schedules
The proposed amendment to §115.729(1) would add pressure relief valves
as applicable devices. Additionally, the proposed amendment to §115.729(1)(A)
would specify that the compliance schedule applies to testing and monitoring
of vent gas streams and pressure relief valves and that the results must be
submitted to the Houston regional office. The proposed amendment to §115.729(1)(A)
would also specify that for vent gas streams and pressure relief valves that
become subject to the requirements of the division after December 31, 2005,
testing and monitoring must be conducted as soon as practicable, but no later
than 60 days after being brought into HRVOC service. The proposed amendment
to §115.729(1)(B) would specify that the owner or operator shall demonstrate
compliance with all other requirements of the division applicable to pressure
relief valves in addition to vent gas streams as soon as practicable but no
later than April 1, 2006.
The proposed amendment to §115.729(2) would correct a cross-reference,
and would specify that for flares that become subject to the requirements
of the division after December 31, 2005, testing and monitoring must be conducted
as soon as practicable but no later than 60 days after being brought into
HRVOC service.
Division 2, Cooling Towers
Section 115.760, Applicability and Cooling Tower
Heat Exchanger System Definitions
The proposed amendment to §115.760 would include non-substantive language
changes to §115.760(a) and (b).
Section 115.761, Site-wide Cap
The commission proposes to amend this section to allow sites the flexibility
of compliance with the cooling tower heat exchange system control requirements
of this division through compliance with the HRVOC emissions cap and trade
program. The proposed amendment to §115.761(a) would change the long-term
site-wide cap strategy to a calendar year basis instead of the existing 24-hour
rolling average basis, and would state that owners or operators of a site
subject to the HRVOC cooling tower heat exchange system rules shall comply
with the HRVOC emissions cap and trade program in Chapter 101, Subchapter
H, Division 6. The proposed amendment to §115.761(a) would also remove
the reference to the site-cap limits in the tables of the SIP. The proposed
amendment would reletter §115.761(b) to §115.761(d). Proposed new §115.761(b)
would specify that all sites subject to this division or to Division 1 that
are exempt from the HRVOC emissions cap and trade program in accordance with §101.392
are limited to ten tons of HRVOC emissions per calendar year. Proposed new §115.761(c)
would provide a short-term, not-to-exceed limit, in pounds of HRVOC per one-hour
block, for all sites subject to this division. The commission continues to
evaluate the magnitude of the short-term limit, and the time period over which
this short-term limit would be enforced. The commission solicits comment regarding
the appropriate level for this short-term limit, and requests any supporting
data regarding alternatives to the magnitude and time period. Proposed new §115.761(c)(3)
would address how exceedances of the short-term limits should be calculated
to determine compliance with the long-term cap.
Section 115.764, Monitoring and Testing Requirements
The proposed amendment to §115.764 would change the section title
from "Monitoring Requirements" to "Monitoring and Testing Requirements" to
reflect the proposed inclusion of the testing requirements formerly in §115.766.
Merging the testing requirements of §115.766 with the monitoring requirements
of §115.764 would provide more consistency with the rule structure of
Subchapter H, Division 1.
The proposed amendment to §115.764(a) would remove the
de minimus
exemption for 100 parts per million, by weight (ppmw) of
HRVOC in the process side fluid. The 100 ppmw
de
minimus
exemption language is proposed to be incorporated into the
appropriate exemptions in §115.767, Exemptions, formerly §115.768,
to better facilitate interpretation of the rule.
The proposed amendment to §115.764(a)(2) would include the calibration
requirements of the total strippable VOC monitoring system from §115.766(1).
The proposed revisions to calibration requirements of the total strippable
VOC monitor in §115.764(a)(2) would include changing the allowable monitor
drift from 3.0% to 5.0%. Furthermore, the proposed amendment would remove
the ten parts per billion, by weight detection limit requirement for the total
strippable VOC monitor. Finally, the proposed amendment to §115.764(a)(2)
would correct the citation to the air-stripping method in Appendix P.
The proposed amendment to §115.764(a)(3) would specify the calculation
methodology to determine the percent measurement data availability, would
provide consistency for the calculation of monitor uptime, and would specify
that time needed for normal calibrations required by the rule is not counted
as downtime. The proposed amendment to §115.764(a)(4) and (5) would replace
the references to §115.766 with the specific reference to the air-stripping
method in Appendix P.
The proposed amendment to §115.764(a)(6) would replace the reference
to "speciation of strippable VOC in paragraphs (4) and (5)" with "speciation
of strippable HRVOC in paragraphs (4) and (5)" because the requirements of §115.764(a)(4)
and (5) are for the speciation of HRVOC only. Additionally, the proposed amendment
would remove the requirement to comply with Section 8.2 of EPA Performance
Specification 9. While the initial testing required under Section 8.2 of Performance
Specification 9 is recommended to help establish proper setup and operation
of the analyzer, the commission considers the calibration requirements specified
in the proposed amendment to §115.764(a)(6) sufficient to quality assure
the data generated by the analyzer, and that it is unnecessary to specifically
require Section 8.2 in the rule. Furthermore, the proposed amendment to §115.764(a)(6)
would change the frequency of the multipoint calibration check procedure in
Section 10.1 of Performance Specification 9 from monthly to quarterly, because
quarterly multipoint calibrations checks provide sufficient quality assurance
of analyzer linearity and accuracy. The proposed amendment to §115.764(a)(6)
would also include non-substantive language revisions to better facilitate
interpretation of the monitoring requirements. Finally, the proposed amendment
to §115.764(a)(6) would specify that periodic sampling during downtime
of the continuous on-line analyzer will continue until the on-line analyzer
is properly operating and within the required performance specifications.
The proposed amendment to §115.764(b) would remove the
de minimus
exemption for 100 ppmw of HRVOC in the process side fluid.
The 100 ppmw
de minimus
exemption language
is proposed to be incorporated into the appropriate exemptions provided in §115.767,
formerly §115.768, to better facilitate interpretation of the rule. The
proposed amendment to §115.764(b)(2) would replace the reference to §115.766
with the specific reference to the air-stripping method in Appendix P.
The proposed amendment to §115.764(b)(3) would add language specifying
the calculation methodology for determining the percent measurement data availability
to provide consistency for the calculation of monitor uptime and specify that
the time required for normal calibrations as required by the rule is not counted
as downtime. The proposed amendment to §115.764(b)(4) and (5) would replace
references to §115.766 specific references to the air-stripping method
in Appendix P. The proposed amendment to §115.764(b)(5) would specify
that additional sampling to determine total strippable VOC, speciated and
total HRVOC must continue on a daily basis until the concentration of total
strippable VOC drops below 50 ppbw.
The proposed amendment to §115.764(b)(6) would remove the reference
to "speciation of strippable VOC" and replace with "speciation of strippable
HRVOC" because the requirements of §115.764(b)(4) and (5) are for speciation
of HRVOC only. Additionally, the proposed amendment would remove the requirement
to comply with Section 8.2 of EPA Performance Specification 9. While the initial
testing required under Section 8.2 of Performance Specification 9 is recommended
to help established proper setup and operation of the analyzer, the commission
considers the calibration requirements specified in the proposed revision
to §115.764(b)(6) sufficient to quality assure the data generated by
the analyzer. Furthermore, the proposed revisions to §115.764(b)(6) would
change the frequency of the multipoint calibration check procedure in Section
10.1 of Performance Specification 9 from monthly to quarterly, because quarterly
multipoint calibrations checks will provide sufficient quality assurance of
analyzer linearity and accuracy. An additional proposed amendment to §115.764(b)(6)
would include non-substantive language revisions to better facilitate interpretation
of the monitoring requirements. Finally, the proposed revisions to §115.764(b)(6)
would specify that periodic sampling during downtime of the continuous on-line
analyzer will continue until the on-line analyzer is properly operating and
within the required performance specifications.
The proposed amendment to §115.764(c) would incorporate language from
the testing requirements in §115.766 that are proposed for repeal. The
proposed amendment would remove the ten ppbw minimum detection limit requirement
for strippable VOC and HRVOC monitoring that currently exists in §115.766(1).
Removing the requirement would provide more flexibility for affected owners
or operators in the selection of on-line monitoring systems and laboratories
for analysis of periodic samples. However, the requirements in proposed new §115.766(a)(3)
and (4) to use one-half the detection limit for HRVOC emission calculation
purposes and the full detection limit for total strippable VOC concentrations
will encourage owners or operators to use a monitoring system or laboratory
analysis with sufficient detection capability appropriate for the specific
cooling tower size and the amount of site-wide caps for the account.
The proposed amendment would delete §115.764(d), regarding requirements
to submit QAPs for the monitoring systems required by §115.764, and move
the requirements for the QAPs to proposed new §115.766(i) in the recordkeeping
and reporting requirements. Also, the proposed amendment would reletter §115.764(e)
to §115.764(d) and replace the reference to the testing requirements
of §115.766 with the reference to the air-stripping method in Appendix
P.
The proposed amendment would reletter §115.764(f), relating to alternatives
to continuous flow monitoring, to §115.764(e), and would correct cross-references
to account for other proposed amendments to the division.
The proposed amendment would reletter §115.764(g), relating to minor
modifications and alternative monitoring, to §115.764(f), would correct
cross-references, and would specify that the provisions for modifications
or alternatives apply to testing as well as monitoring.
Proposed new §115.764(g) would specify that alternative monitoring
locations may be used for cooling tower heat exchanger systems in which a
single cooling tower services both HRVOC and non-HRVOC process units. The
proposed new provisions would allow the owner or operator to monitor from
locations that represent the flow and concentrations from HRVOC processes.
Proposed Repeal of Section 115.766, Testing Requirements
The commission proposes to repeal §115.766 and to incorporate specific
testing requirements of §115.766 into the appropriate subsections in §115.764
to establish more consistency with Division 2 and to better facilitate interpretation
of the proposed requirements.
Proposed Repeal of Section 115.767, Recordkeeping
Requirements
The commission proposes to repeal §115.767 and to incorporate specific
recordkeeping requirements of §115.767 into proposed new §115.766,
Recordkeeping and Reporting Requirements, to establish more consistency with
Division 1.
Section 115.766, Recordkeeping and Reporting Requirement
Proposed new §115.766 incorporates the recordkeeping and reporting
requirements of §115.767 to establish more consistency with Division
1 and more accurately reflect the requirement of the §115.766. Proposed
new §115.766(a)(2) would correct cross-references in existing §115.767(a)(2).
Proposed new §115.766(a)(3) would remove the requirement to maintain
hourly records documenting the pound per hour mass emission rate for total
strippable VOC in existing §115.767(a)(3). The testing and monitoring
requirements in §115.764 for total strippable volatile organic compound,
when applicable, do not require determining the mass emission rate of total
strippable VOC. The recordkeeping requirements for total strippable VOC concentration
are addressed in proposed new §115.766(a)(4). Proposed new §115.766(a)(3)
would also correct cross-references and incorporate recordkeeping requirements
for alternative monitoring provided for in §115.764(a)(6) or (b)(6).
Proposed new §115.766(a)(3) would require owners or operators to use
one-half the minimum detection limits for HRVOC emission calculations when
concentrations are below detection.
Proposed new §115.766(a)(4) would require owner or operators to use
the full minimum detection limit for total strippable VOC when concentrations
are below detection. Removing the ten parts per billion detection limit requirement
would provide more flexibility for affected owner or operators in the selection
of on-line monitoring systems and laboratories for analysis of periodic samples.
However, the requirements to use one-half the detection limit for HRVOC emission
calculation purposes and the full detection limit for total strippable VOC
concentrations will encourage owner or operators to use a monitoring system
or laboratory analysis with sufficient detection capability appropriate for
the specific size of cooling tower and the amount of the side-wide caps for
the account.
Proposed new §115.766(a)(4) would specify recordkeeping requirements
for the concentration of total strippable VOC in the cooling water for cooling
tower heat exchanger systems monitored in accordance with §115.764(b)(2)
or (d). Proposed new §115.766(a)(4) would further specify that if it
concentration results for total strippable VOC are below the minimum detection
limit, then the full detection limit will be used to calculate the average
total strippable VOC concentration in the cooling water.
The proposed amendment to §115.766 would delete the requirements in
existing §115.767(a)(5) regarding hourly recordkeeping requirements for
the 24-hour rolling average HRVOC emissions in relation to the site wide cap.
Provisions for recordkeeping to demonstrate compliance with the site-wide
caps specified in §115.761 are provided in proposed new §115.766(g)
and (h). The proposed amendment also deletes the requirements in existing §115.766(a)(6)
regarding recordkeeping requirements for alternative monitoring performed
in accordance with §115.764(a)(6) or (b)(6). As previously noted, new §115.766(a)(3)
is proposed to incorporate these recordkeeping requirements.
Proposed new §115.766(a)(5) specifies that the owner or operator must
maintain hourly records of the cooling water flow rate. Finally, proposed
new §115.766(a)(6) would remove the term "hourly" from the existing language
of §115.767(a)(4) to specify that owner or operators must maintain records
on a weekly basis.
The proposed amendment to §115.766 includes revisions to §115.766(b)
to correct cross-references in the existing language of §115.767(b).
The proposed language in new §115.767(c) is the same as the language
in existing §115.767(c). Proposed new §115.766(d) includes existing
language from §115.767(d)(1) and (2) to reflect proposed new §115.766(a)
incorporating the recordkeeping requirements for testing performed in accordance
with §115.764(d) and to better facilitate interpretation of the recordkeeping
requirements.
Proposed new §115.766(e) and (f) would correct cross-references in
existing §116.767(e) and (f).
Proposed new §115.766(g) and (h) would specify recordkeeping requirements
to demonstrate compliance with §115.761. Proposed new §115.766(g)
would specify recordkeeping requirements to demonstrate compliance with tons
per calendar year emission limits in §115.761(a) and (b). Proposed new §115.766(h)
would recordkeeping requirements to demonstrate compliance with pound per
hour emission limits in §115.761(c).
Finally, proposed new §115.766(i) would incorporate the requirements
for submitting QAPs for monitoring performed in accordance with §115.764.
The requirements for submitting QAPs is proposed to be moved from §115.764(d)
to the recordkeeping and reporting requirements in §115.766 to more appropriately
represent the requirement and to be more consistent with the rule structure
of Division 1. In addition, proposed new §115.766(i)(2) would change
the requirement to submit the QAP at least 60 days prior to the cooling tower
heat exchange system being placed into service to a requirement that the quality
assurance plan must be submitted prior to the system being placed into HRVOC
service. The proposed amendment would also remove the requirement in existing §115.764(d)(2)
that specifies that the plan must be submitted prior to initiating a monitoring
program to comply with the requirements of §115.764. The proposed amendment
to move the quality assurance plan provisions to §115.766(i) would also
remove the requirement in §115.764(d)(2) to define each compound that
could potentially leak through the heat exchanger. Finally, proposed new §115.766(j)
would specify that an owner or operator claiming exemption under §115.767(4)
shall submit written notification at least 15 days prior to permanently removing
a flare from service, but no later than December 31, 2005.
Section 115.767, Exemptions
The commission proposes to repeal §115.768 and to incorporate exemptions
of §115.768 into the appropriate subsections in proposed new §115.767
to be consistent with the section numbering in Division 1. Proposed new §115.767(1)
and (2) would specify that the exemptions apply to heat exchangers with greater
than 100 ppmw HRVOC in the process side fluid. Also, the commission proposes
to delete the exemption in existing §115.768(4), because emissions events
are not exempt from §115.761 in this proposal. Proposed new §115.767(4)
would specify that cooling tower heat exchange systems that will be permanently
out of service by April 1, 2006, are exempt from the requirements of the division,
except for the recordkeeping requirements of §115.766(j). The proposed
new exemption will provide relief for owners or operators with cooling tower
heat exchange systems that will be permanently taken out of service after
the December 31, 2005 compliance date for installation of continuous monitoring
equipment, but prior to the April 1, 2006 compliance date for the site-wide
caps in §115.761.
Section 115.769, Counties and Compliance Schedules
The proposed amendment to §115.769 would update cross-references and
add new §115.769(b) to address the compliance date requirements for cooling
tower heat exchange systems that become subject to the requirements of the
division after December 31, 2005.
Division 3, Fugitive Emissions
Section 115.780, Applicability
The proposed amendment to §115.780 would designate the first paragraph
as subsection (a) and would add new §115.780(b) to specify that emission
reduction credits or discrete emission reduction credits may not used in order
to demonstrate compliance with the HRVOC fugitive emissions rules.
Section 115.781, General Monitoring and Inspection
Requirements
The proposed amendment to §115.781(b)(1) would update a cross-reference
to specify that the exemptions of §115.357(1) - (11) are not applicable
to this division. The term "immediately" is proposed to be added to §115.781(b)(7)(A),
to specify that if requested by staff of the Houston regional office or any
air pollution control agency having jurisdiction, the owner or operator must
provide the account's unsafe-to-monitor list within that business day. The
proposed amendment to §115.781(b)(7)(B) would specify that difficult-to-monitor
components include components that are located below flooring or deck grating
that would require confined space entry as defined in 29 CFR §1910.146,
concerning Permit-required confined spaces (December 1, 1998).
The proposed amendment to §115.781(b)(8) and (e) would specify that
all pressure relief valves in gaseous service must be monitored with a hydrocarbon
gas analyzer for fugitive leaks. The intent of the change is to specify that
the body of the pressure relief valve should be monitored for fugitives on
a quarterly basis and within 24 hours following actuation, and not to require
the monitoring of the vent from the pressure relief valve. The emissions associated
with the venting of the pressure relief valve due to a pressure exceedance
in the process is addressed in the Subchapter H, Division 1 proposal. However,
the quarterly monitoring or other required fugitive monitoring should include
a check with a hydrocarbon gas analyzer to ensure that the relief mechanism
has properly reseated.
Proposed new §115.781(g) would add language regarding data collection
that is similar to data collection language in Subchapter D, §115.354(10).
The language is proposed to be removed from §115.354(10) in concurrent
rulemaking. These changes are being proposed at the request of industry. The
commission seeks comment on these proposed changes.
Section 115.782, Procedures and Schedule for Leak
Repair and Follow-up
The proposed amendment to §115.782(c) would specify that components
on the delay of repair list that would require a shutdown to correct, must
be repaired at the next scheduled process unit shutdown. The proposed amendment
to §115.782(c)(1)(B)(i) would replace the current language with language
requiring documentation of calculations in §115.782(c)(1)(B)(i) - (iii),
and would renumber clause (ii) as clause (iv). The proposed language in §115.782(c)(1)(B)(i)
- (iii) is similar to language that is proposed to be removed from Subchapter
D, §115.352(2)(A)(i) - (iii), in concurrent rulemaking, and the proposed
amendment is at the request of industry. The commission seeks comment on these
proposed changes.
The proposed amendment to §115.782(c)(2)(A)(i) would specify that
extraordinary efforts must be taken within 14 or 30 calendar days after the
leak is found (depending on the amount of the leak detected), instead of seven
or 15 days of the valve being placed on the shutdown list. The proposed amendment
does not allow any additional days nor reduce the number of days, but simply
revises the language to a time frame that the owner or operator will more
readily know from the information already in the databases.
Section 115.783, Equipment Standards
The proposed amendment to §115.783(2) would delete the language that
recovery devices, flares, and other control devices that are used to control
fugitive emissions must obtain a set control efficiency. This language is
proposed to be deleted because the emissions from these types of sources are
already being controlled or are proposed to be controlled by Subchapter B,
Division 2 rules or by Subchapter H, Division 1 rules. The proposed amendment
to §115.783(3) would delete the requirement that a pressure relief valve
must be equipped with a pressure sensing device. This language is proposed
to be deleted because the emissions from these types of sources would be controlled
by Subchapter H, Division 1. The proposed amendment to §115.783 would
renumber paragraphs (4) - (6) as paragraphs (3) - (5).
Proposed Repeal of §115.785, Testing Requirements
The commission proposes to repeal §115.785 because the section established
a stack testing method for sources that control fugitive emissions. These
sources are controlled or proposed to be controlled under Subchapter H, Division
1; therefore, these additional requirements are no longer necessary in the
fugitive rules.
Section 115.786, Recordkeeping Requirements
The proposed amendment to §115.786(b)(3)(D) would specify that the
flow through the bypass line is an estimated flow rate. The proposed amendment
to §115.786(c) would specify the exact date that specific records must
be submitted to the Houston regional office and any local air pollution control
agency having jurisdiction.
The proposed amendment to §115.786(d) and (e) would specify that the
type of records used to identify exempt components is the same as the type
of records listed in §115.781. Proposed new §115.786(d)(1) and (2)
would add similar language that is proposed to be removed from Subchapter
D, §115.352(2)(F)(ix) and §115.356(3) in concurrent rulemaking.
The proposed amendment to §115.786 would also reletter subsection (e)
to subsection (f). The commission seeks comment on these proposed changes.
Section 115.787, Exemptions
The proposed amendment to §115.787(a) would correct a citation from §115.786(d)
and (e) to §115.786(e) and (f), and the proposed amendment to §115.787(b)
would correct a citation from §115.783(4) to §115.783(2).
The proposed amendment to §115.787(c)(4) would change the language
"plant sites covered by a single account number" to "any account." The proposed
amendment to §115.787(c)(6) and (7) would replace the phrase "which are
in compliance with" with the phrase "that meet the requirements of" because
the current language may be incorrectly interpreted as requiring direct compliance
with the selected provisions of 40 CFR §63.166 or §63.169.
The commission proposes to delete §115.787(e), because the control
of vents of pressure relief valves is being proposed in the amendments to
Subchapter H, Division 1 and is no longer needed in this division. The proposed
amendment to §115.787 would also reletter subsection (f) to subsection
(e).
Proposed new §115.787(f) would reletter the subsection to §115.787(e),
and correct a citation from §115.352(4) to §115.783(5).
Proposed new §115.787(f) would exempt any process unit with less than
50 components in HRVOC service from the third-party audit requirements of §115.788.
Section 115.788, Audit Provisions
The proposed amendment to §115.788(a) would change the time frame
and number of process units for which the independent third-party audits must
be conducted. The proposed amendment would change the requirement to conduct
an audit of all process units every two years to a requirement to conduct
an audit of at least one process unit at least once per calendar year. In
addition, the amendment would require that all process units at an account
must be audited at least once every five calendar years. Accounts with less
than five process units but more than one process unit, should not audit the
same unit two years in a row.
The proposed amendment to §115.788(a)(1) would require the independent
third-party organization to verify that all components are properly tagged
in accordance with §115.782(a). The proposed amendment to §115.788(a)(1)(B)
and (d)(2) would remove the requirement for the audit to include a list of
components that should have been monitored but were not on the list to be
monitored. The reasoning for the proposed amendment is that the existing language
would require the company conducting the audit to completely inspect the entire
process unit, including, but not limited to, steam lines, water lines, and
waste lines. The commission considers this requirement to be cost prohibitive
for the results that would be obtained.
The proposed amendment to §115.788(a)(2) would state that independent
third-party organization must perform a field survey to determine the representative
percentage of leaking components in the audited process unit. The proposed
amendment to §115.788(a)(2)(A) would also specify that the field survey
must be started after the usual monitoring service has completed its monitoring
of the process unit and that the field survey conducted by the auditing company
must be completed by the end of the monitoring period (i.e., quarterly) in
which the usual monitoring service conducted its monitoring. The proposed
amendment to §115.788(a)(2)(B) would remove superfluous language.
The proposed amendment to §115.788(a)(2)(C) would replace the term,
"audit" with the term, "field survey" and further specify that the field survey
of a specific process unit must not include components from the most recent
field survey of that process unit. Proposed new §115.788(a)(2)(D) specifies
that the independent third-party organization must follow Test Method 21 in
40 CFR Part 60, Appendix A, while conducting the field survey.
The proposed amendment to §115.788(a)(3) would specify that the data
generated by monitoring technicians must be reviewed by the independent third-party
organization. The proposed amendment to §115.788 would also consolidate
the language in §115.788(a)(3)(A) and(B), and would move the language
in §115.788(d)(4) to §115.788(a)(3)(A). The proposed amendment to §115.788(a)(3)(B)
would require that the independent third-party organization review the records
to verify proper calibration in accordance with Test Method 21. The proposed
amendment to §115.788(a)(3)(C) would delete the term, "abnormal" and
specify that the requirement is to identify data patterns indicative of failure
to properly implement Test Method 21. The proposed amendment would delete §115.788(a)(3)(D)
because the retention of field data from a datalogger is not specifically
required.
The proposed amendment to §115.788(b) would make a grammatical correction
to remove the term "means" and replace it with the term "is."
The proposed amendment to §115.788(c) would remove the requirement
to provide the agency written notification that the audit has been completed.
The requirement is unnecessary, because the owner or operator is already required
to provide the results of the audit to the Houston regional office within
30 days after completion of the audit.
The proposed amendment to §115.788(d) would specify that the audit
report should be submitted to the Houston regional office, instead of the
more general description of the Office of Compliance and Enforcement or appropriate
regional office. The proposed amendment to §115.788(d)(1) would specify
that the list concerning the components that were not tagged but should have
been, is based on the requirements of §115.782(a).
The proposed amendment to §115.788(d) would renumber paragraphs (3)
and (4) to paragraphs (2) and (3), and the proposed amendment to renumbered §115.788(d)(2)
would specify that the percentage of leaking components should be identified
during the field survey.
The proposed amendment to renumbered §115.788(d)(3) would delete subparagraphs
(A) - (C) and reference the categories specified in §115.788(a)(3)(A)
- (C).
Proposed new §115.788(e) would require the owner or operator to submit
a corrective action plan with the audit report if the results of the audit
indicate deficiencies in the implementation of Test Method 21. Subsections
(e) and (f) are also proposed to be relettered as subsections (f) and (g).
Finally, proposed new §115.788(h) would specify that the executive
director may require additional corrective actions.
Section 115.789, Counties and Compliance Schedules
The proposed amendment to §115.789(3) would specify that the initial
third-party audits required in §115.788 must be completed as soon as
practicable, but no later than December 31, 2005. The proposed deletion of
the current §115.789(4) would remove the compliance schedules for testing
requirements, because the corresponding testing requirements in §115.785
are proposed to be repealed. The proposed amendment to §115.789 would
renumber paragraphs (5) and (6) to paragraphs (4) and (5).
FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT
Nina Chamness, Analyst, Strategic Planning and Appropriations Section,
determined that for the first five-year period the proposed rulemaking is
in effect, there will not be significant fiscal implications for the agency
or other units of state and local government as a result of administration
or enforcement of the proposed rulemaking.
The proposed rulemaking affects regulated entities in the HGA that conduct
activities that emit HRVOC. State and local governments do not engage in these
activities, so they are not affected by the proposed rulemaking.
The proposed rulemaking only affects the petrochemical, chemical, loading,
and refinery companies in the HGA. The major impacts of the proposed rulemaking
are as follows: 1) caps on HRVOC allowances are lowered, thereby requiring
some companies to emit less HRVOC; 2) adds parameter monitoring requirements
for pressure relief valves and vent gas streams not routed to a flare. Companies
can decide which process parameters to monitor as long as the process parameters
satisfy the proposed requirements; 3) includes alternative provisions for
specific flare categories such as emergency flares, flares in temporary HRVOC
service, and flares designed to receive and control liquid or dual phase streams.
These provisions will reduce current monitoring costs; and 4) for companies
with greater than two process units, reduces the number of independent, third-party
audits of processes in HRVOC service that generate fugitive emissions.
PUBLIC BENEFITS AND COSTS
Ms. Chamness also determined that for each year of the first five years
the proposed rulemaking is in effect, the public benefit anticipated from
the changes seen in the proposed rulemaking will be the reduction of HRVOC
emissions in the HGA. This will allow Texas to comply with the SIP required
by 42 USC and reduce the ozone levels in this nonattainment area to levels
determined by the EPA to be necessary for a healthy and safe environment.
The commission anticipates fiscal impacts for businesses and individuals
in the petrochemical, chemical, loading, and refining industries in the HGA;
however, the commission anticipates that the changes in monitoring requirements
would not result in significant fiscal implications. Provisions that reduce
the HRVOC emissions for compliance with the site-wide cap in Harris County
may have significant fiscal implications for these industries, depending upon
the methodology used to reduce the HRVOC emissions.
Revised Monitoring Requirements
The proposed rulemaking reduces the requirements for independent, third-party
audits of each process that generates fugitive emissions. The commission conservatively
estimates that the current audit provision would require affected industries
to pay for 400 to 500 audits every two years at a cost of approximately $5,000
- $10,000 per audit. The proposed rulemaking would require independent, third-party
audits of a minimum of one process unit per year per account. Depending on
the size of the account, the proposed rulemaking could present a significant
cost savings to some accounts. For example, under the current rules an account
with 40 process units would be required to perform all 40 audits within two
years. The proposed rulemaking would require the 40 audits to be performed
within a five-year period. The commission estimates that these audits would
cost approximately $200,000 - $400,000 over a two-year period. In this example,
the cost savings attributed to the proposed rulemaking would be approximately
$120,000 - $240,000 during the two-year period. The commission anticipates
that the cost savings from reducing the audit provisions would help mitigate
any costs associated with additional monitoring that the proposed rulemaking
would require.
The proposed rulemaking adds parameter monitoring requirements for pressure
relief valves and vent gas streams that are not routed to a flare. The proposed
rulemaking provides flexibility on the process parameters that can be monitored
as long as the process parameters satisfy the proposed requirements. Thus,
companies have some control over the cost of the new monitoring requirements.
The commission anticipates that in some cases, parameters that meet the proposed
requirements may already be monitored. If a suitable parameter is already
being monitored, but is not currently being recorded, companies may be able
to make minor modifications to existing process monitoring to comply with
the proposed monitoring requirements. Therefore, significant additional monitoring
costs should not be incurred.
The proposed rulemaking adds alternatives to the continuous monitoring
requirements for specific flare categories, such as emergency flares, flares
in temporary HRVOC service, and flares designed to receive and control liquid
or dual-phase streams. Under current rules, these flares are subject to the
full continuous monitoring requirements including continuously measuring HRVOC.
However, for these flare categories, such monitoring may be impractical due
to the infrequent use or the nature of the streams sent to the flare. The
proposed rulemaking would allow companies to use alternatives, such as process
knowledge and engineering calculations, or process knowledge and engineering
calculations combined with process parameter monitoring. These proposed alternatives
will result in cost savings for owners or operators of the flare categories.
Emissions Compliance
The commission anticipates that HRVOC emissions reductions for compliance
with the site-wide cap in Harris County will have a significant fiscal impact
on the petrochemical, chemical, and refining industries. The proposed rulemaking
would require an additional 57% reduction of HRVOC emissions in the site-wide
cap for Harris County. Furthermore, the proposed rulemaking will include emissions
in the cap from emission events and scheduled startup, shutdown, and maintenance
activities.
At least 93 Harris County sites may incur significant costs when complying
with the proposed cap. Because companies are given flexibility in how to achieve
cap compliance, the commission staff is unable to provide a total cost estimate
per process or per site. Costs will vary widely depending on the methodology
each company employs to reduce their HRVOC emissions. If the additional reductions
require a company to install an additional control device for previously uncontrolled
vent gas streams, the estimated capital and annual operating costs for a control
device could be approximately $600,000 and $360,000 respectively, based on
fiscal information provided in the 2002 HRVOC rule proposal.
SMALL BUSINESS AND MICRO-BUSINESS ASSESSMENT
The commission has been unable to identify any small or micro-businesses
which would be affected by the proposed rulemaking. The majority of sites
affected by the proposed rulemaking are large petrochemical and industrial
businesses. If there are affected small or micro-businesses, the estimated
capital and annualized cost in this fiscal note would be a reasonable cost
estimate for small or micro-businesses.
LOCAL EMPLOYMENT IMPACT STATEMENT
The commission reviewed this proposed rulemaking action and determined
that a local employment impact statement is not required because the proposed
rulemaking does not adversely affect a local economy in a material way for
the first five years that the proposed rulemaking is in effect.
DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION
The commission reviewed the proposed rulemaking action 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. A "major environmental rule"
is 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, productivity, competition, jobs, the environment,
or the public health and safety of the state or a sector of the state.
The proposed rulemaking action to Chapter 115 and revisions to the SIP
would improve implementation of the existing Chapter 115 by adding requirements
to achieve reductions in HRVOC emissions in the HGA. The rules are intended
to protect the environment and reduce risks to human health and safety from
environmental exposure and may have adverse effects on owners and operators
of certain sources, in particular fugitives, flares, process vents, and cooling
towers. Many of these sources are owned or operated by utilities, petrochemical
plants, refineries, and other industrial, commercial, or institutional groups,
and each group could be considered a sector of the economy. This determination
is based on the analysis provided elsewhere in this preamble, including the
discussion in the PUBLIC BENEFITS AND COSTS section of this proposal. The
remaining amendments in this rulemaking are intended to correct typographical
errors, update cross-references, add flexibility and delete obsolete language,
and these amendments are not expected to 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.
This proposed rulemaking does not meet any of the four applicability criteria
of a "major environmental rule" as defined in the Texas Government Code. Texas
Government Code, 2001.0225 applies only to a major environmental rule
the result of which is to: 1) exceed a standard set by federal law, unless
the rule is specifically required by state law; 2) exceed an express requirement
of state law, unless the rule is specifically required by federal law; 3)
exceed a requirement of a delegation agreement or contract between the state
and an agency or representative of the federal government to implement a state
and federal program; or 4) adopt a rule solely under the general powers of
the agency instead of under a specific state law.
The rulemaking implements requirements of 42 USC. Under 42 USC, §7410,
states are required to adopt a SIP that provides for "implementation, maintenance,
and enforcement" of the primary national ambient air quality standards (NAAQS)
in each air quality control region of the state. While 42 USC, §7410,
does not require specific programs, methods, or reductions in order to meet
the standard, 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, such as 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 to attain the NAAQS for
the specific regions in the state. Even though 42 USC allows states to develop
their own programs, this flexibility does not relieve a state from developing
a program that meets the requirements of 42 USC, §7410. Thus, while specific
measures are not generally required, the emission reductions are required.
States are not free to ignore the requirements of 42 USC, §7410, and
must develop programs to assure that the nonattainment areas of the state
will be brought into attainment on schedule.
The requirement to provide a fiscal analysis of proposed regulations in
the Texas Government Code were amended by Senate Bill (SB) 633 during the
75th Legislature (1997). The intent of SB 633 was to require agencies to conduct
an 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 discussed earlier
in this preamble, 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 in its fiscal notes. Because the legislature
is presumed to understand the fiscal impacts of the bills it passes, and that
presumption is based on information provided by state agencies and the Legislative
Budget Board, 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
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.
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
the HGA. The proposed rules, that will reduce ambient HRVOC and ozone in the
HGA, will be submitted to the EPA as one of several measures in the federally
approved SIP. As discussed earlier in this preamble, controls on upsets and
routine industrial VOC emissions are necessary to address some of the elevated
ozone levels observed in the HGA; these controls will result in reductions
in ozone formation in the HGA and help bring the HGA into compliance with
the air quality standards established under federal law as NAAQS for ozone.
As discussed in Chapter 6 of the HGA SIP, this revision is another phase in
the process of continued analysis and review of the science, and the data
collected as a result of these revisions will further assist the commission
as it develops its full reassessment of the attainment demonstration at the
midcourse review. Therefore, the proposed rulemaking is a necessary component
of and consistent with the HGA ozone attainment demonstration SIP required
by 42 USC, §7410.
The commission has consistently applied this construction to its rules
since this statute was enacted in 1997. Since that time, the legislature has
revised the Texas Government Code but left this provision substantially unamended.
The commission presumes that "when an agency interpretation is in effect at
the time the legislature amends the laws without making substantial change
in the statute, the legislature is deemed to have accepted the agency's interpretation."
As discussed earlier in this preamble, this rulemaking action implements
requirements of 42 USC. There is no contract or delegation agreement that
covers the topic that is the subject of this action. Therefore, the proposed
rulemaking does not exceed a standard set by federal law, exceed an express
requirement of state law, exceed a requirement of a delegation agreement,
nor adopted solely under the general powers of the agency. Finally, this rulemaking
action was not developed solely under the general powers of the agency, but
is authorized by specific sections of Texas Health and Safety Code, Chapter
382 (also known as the Texas Clean Air Act), and Texas Water Code that are
cited in the STATUTORY AUTHORITY section of this preamble, including Texas
Health and Safety Code, §§382.011, 382.012, 382.014, 382.016, 382.017,
382.021, and 382.034. Therefore, this rulemaking action is not subject to
the regulatory analysis provisions of Texas Government Code, §2001.0225(b),
because the proposed rulemaking does not meet any of the four applicability
requirements. The commission invites public comment on the draft RIA determination.
TAKINGS IMPACT ASSESSMENT
The commission completed a takings impact analysis for the proposed rulemaking
action under Texas Government Code, §2007.043. The specific purposes
of this rulemaking are to achieve reductions of HRVOC emissions and ozone
formation in the HGA and help bring the HGA into compliance with the air quality
standards established under federal law as NAAQS for ozone, as well as to
improve implementation of the existing Chapter 115 by correcting typographical
errors, updating cross-references, clarifying ambiguous language, adding flexibility,
and deleting obsolete language. If adopted, certain sources located in the
HGA will be required to install equipment to monitor emissions and achieve
HRVOC emission reductions in the HGA, and implement new reporting and recordkeeping
requirements. Installation of the necessary equipment could conceivably place
a burden on private, real property.
Texas Government Code, §2007.003(b)(4), provides that Chapter 2007
does not apply to this proposed rulemaking action, because it is reasonably
taken to fulfill an obligation mandated by federal law. The emission limitations
and control requirements within this rulemaking action 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 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, one purpose of this rulemaking action is to
meet the air quality standards established under federal law as NAAQS. Attainment
of the ozone standard will eventually require reductions of HRVOC emissions,
as well as substantial reductions in NO
x
emissions.
Any VOC reductions resulting from the current rulemaking are no greater than
what scientific research indicates is necessary to achieve the desired ozone
levels. However, this rulemaking is only one step among many necessary for
attaining the ozone standard.
In addition, Texas Government Code, §2007.003(b)(13), states that
Chapter 2007 does not apply to an action that: 1) is taken in response to
a real and substantial threat to public health and safety; 2) is designed
to significantly advance the health and safety purpose; and 3) does not impose
a greater burden than is necessary to achieve the health and safety purpose.
Although the 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 significantly advance the health and safety
purpose. This action is taken in response to the HGA exceeding the federal
ozone NAAQS, that adversely affects public health, primarily through irritation
of the lungs. The action significantly advances the health and safety purpose
by reducing ozone levels in the HGA. Consequently, these proposed rules meet
the exemption in §2007.003(b)(13). This rulemaking action therefore meets
the requirements of Texas Government Code, §2007.003(b)(4) and (13).
For these reasons, the proposed rules do not constitute a takings under Chapter
2007.
CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM
The commission reviewed the proposed rulemaking action and found that the
proposal is an action identified in Coastal Coordination Act Implementation
Rules, 31 TAC §505.11, or will affect an action/authorization identified
in §505.11, and therefore will require that applicable goals and policies
of the Coastal Management Program (CMP) be considered during the rulemaking
process.
The commission determined that under 31 TAC §505.22 the proposed rulemaking
action is consistent with the applicable CMP goals and policies. The CMP goal
applicable to this rulemaking action is the goal to protect, preserve, and
enhance the diversity, quality, quantity, functions, and values of coastal
natural resource areas (31 TAC §501.12(1)). No new sources of air contaminants
will be authorized and ozone levels will be reduced as a result of the proposed
rulemaking. 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. 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.
EFFECT ON SITES SUBJECT TO THE FEDERAL OPERATING PERMIT PROGRAM
Chapter 115 is an applicable requirement under 30 TAC Chapter 122; therefore,
owners or operators subject to the Federal Operating Permit Program must,
consistent with the revision process in Chapter 122, revise their operating
permits to include the revised Chapter 115 requirements for each emission
unit affected by the revisions to Chapter 115 at their sites.
ANNOUNCEMENT OF HEARINGS
Public hearings for this proposed rulemaking have been scheduled for the
following times and locations: August 2, 2004, 1:30 p.m. and 5:30 p.m., City
of Houston, City Council Chambers, 2nd Floor, 901 Bagby, Houston; August 3,
2004, 10:30 a.m., John Gray Institute, 855 Florida Avenue, Beaumont; and August
5, 2004, 9:30 a.m., Texas Commission on Environmental Quality, 12100 North
I-35, Building F, Room 2210, Austin. The hearings will be structured for the
receipt of oral or written comments by interested persons. Registration will
begin 30 minutes prior to the hearings. Individuals may present oral statements
when called upon in order of registration. A time limit may be established
at the hearings to assure that enough time is allowed for every interested
person to speak. There will be no open discussion during the hearings; however,
commission staff members will be available to discuss the proposal 30 minutes
before the hearings and will answer questions before and after the hearings.
Persons planning to attend the hearings who have special communication
or other accommodation needs, 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 Patricia Durón, MC 205, Office
of Environmental Policy, Analysis, and Assessment, Texas Commission on Environmental
Quality, P.O. Box 13087, Austin, Texas 78711-3087, faxed to (512) 239-4808,
or emailed to
siprules@tceq.state.tx.us
. All
comments should reference Rule Project Number 2004-037-115-AI. Comments must
be received by 5:00 p.m., August 9, 2004. For further information, please
contact Ashley Forbes of the Environmental Planning and Implementation Division
at (512) 239-0493 or Alan Henderson, of the Policy and Regulations Division,
at (512) 239-1510.
Subchapter A. DEFINITIONS
30 TAC §115.10
STATUTORY AUTHORITY
The amendments are proposed under Texas Water Code, §5.103, concerning
Rules, and §5.105, concerning General Policy, that authorize the commission
to adopt rules necessary to carry out its powers and duties under the Texas
Water Code; and under Texas Health and Safety Code, §382.017, concerning
Rules, that authorizes the commission to adopt rules consistent with the policy
and purposes of the Texas Clean Air Act. The amendments are also proposed
under Texas Health and Safety Code, §382.002, concerning Policy and Purpose,
that establishes the commission's purpose to safeguard the state's air resources,
consistent with the protection of public health, general welfare, and physical
property; §382.011, concerning General Powers and Duties, that authorizes
the commission to control the quality of the state's air; §382.012, concerning
State Air Control Plan, that authorizes the commission to prepare and develop
a general, comprehensive plan for the proper control of the state's air; and §382.016,
concerning Monitoring Requirements Examination of Records, that authorizes
the commission to prescribe reasonable requirements for measuring and monitoring
the emissions of air contaminants.
The proposed amendments implement Texas Health and Safety Code, §§382.002,
382.011, 382.012, and 382.017.
§115.10.Definitions.
Unless specifically defined in
Texas Health and Safety Code, Chapter
382, (also known as the Texas Clean Air Act)
[
(1)
Background--The ambient concentration of volatile organic
compounds [
(2)
(No change.)
(3)
Capture efficiency--The amount of
volatile organic
compounds (VOC)
[
(4) - (5)
(No change.)
(6)
Component--A piece of equipment, including, but not limited
to, pumps, valves, compressors, connectors, and pressure relief valves, which
has the potential to leak
volatile organic compounds
[
(7) - (11)
(No change.)
(12)
Emergency flare--A flare that only receives
emissions during an upset event or unscheduled maintenance, startup, or shutdown
activity.
(13)
[
(14)
[
(15)
[
(16)
[
(17)
[
(18)
[
(A)
In Harris County, one or more of the following
volatile
organic compounds (VOCs)
[
(B)
In Brazoria, Chambers, Fort Bend, Galveston, Liberty, Montgomery,
and Waller Counties, one or more of the following VOCs: ethylene and propylene.
(19)
[
(20)
[
(21)
[
(22)
[
(23)
[
(24)
[
(25)
[
(26)
[
(27)
[
(28)
[
(29)
[
(30)
[
(31)
[
(32)
[
(33)
[
(A)
a rupture disk; or
(B)
a conservation vent or other device on an atmospheric storage
tank that is actuated either by a vacuum or a pressure of no more than 2.5
pounds per square inch gauge [
(34)
[
(35)
[
(36)
[
(37)
[
(38)
[
(A)
The term shutdown or turnaround does not include a work
practice that would stop production from a process unit or part of a unit:
(i)
for less than 24 hours; or
(ii)
for a shorter period of time than would be required to
clear the process unit or part of the unit and start up the unit.
(B)
Operation of a process unit or part of a unit in recycle
mode (i.e., process material is circulated, but production does not occur)
is not considered shutdown.
(39)
[
(40)
[
[(A)
the method in Appendix P of the Texas
Commission on Environmental Quality (commission) Sampling Procedures Manual,
January 2003;]
[(B)
a method approved by the executive director
that can produce equivalent results as compared to the method in Appendix
P; or]
[(C)
a method approved by the executive director
that determines VOCs emitted from the cooling tower by VOC mass balance across
the cooling tower.]
(41)
[
(42)
[
(43)
[
(44)
[
(45)
[
(46)
[
(47)
[
(48)
[
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 June 25, 2004.
TRD-200404255
Stephanie Bergeron
Director, Environmental Law Division
Texas Commission on Environmental Quality
Earliest possible date of adoption: August 8, 2004
For further information, please call: (512) 239-6087
1.
VENT GAS CONTROL
30 TAC §§115.720, 115.722, 115.725 - 115.727, 115.729
STATUTORY AUTHORITY
The amendments are proposed under Texas Water Code, §5.103, concerning
Rules, and §5.105, concerning General Policy, that authorize the commission
to adopt rules necessary to carry out its powers and duties under the Texas
Water Code; and under Texas Health and Safety Code, §382.017, concerning
Rules, that authorizes the commission to adopt rules consistent with the policy
and purposes of the Texas Clean Air Act. The amendments are also proposed
under Texas Health and Safety Code, §382.002, concerning Policy and Purpose,
that establishes the commission's purpose to safeguard the state's air resources,
consistent with the protection of public health, general welfare, and physical
property; §382.011, concerning General Powers and Duties, that authorizes
the commission to control the quality of the state's air; §382.012, concerning
State Air Control Plan, that authorizes the commission to prepare and develop
a general, comprehensive plan for the proper control of the state's air; and §382.016,
concerning Monitoring Requirements Examination of Records, that authorizes
the commission to prescribe reasonable requirements for measuring and monitoring
the emissions of air contaminants.
The proposed amendments implement Texas Health and Safety Code, §§382.002,
382.011, 382.012, and 382.017.
§115.720.Applicability and Definitions.
(a)
Applicability. In the Houston/Galveston area, as defined
in §115.10 of this title (relating to Definitions), any account with
a
controlled or uncontrolled
vent gas stream containing highly-reactive
volatile organic compounds (HRVOC), as defined in §115.10 of this title,
or a flare that emits or has the potential to emit HRVOC is subject to this
division (relating to Vent Gas Control) in addition to the applicable requirements
of Subchapter B, Divisions 2 and 6 of this chapter (relating to Vent Gas Control;
and Batch Processes) and Subchapter D, Division 1 of this chapter (relating
to Process Unit Turnaround and Vacuum-Producing Systems in Petroleum Refineries).
(b)
Definitions. The following terms, when used in this division,
[
(1)
Degassing safety device--A device other
than a flare used to prevent the release of unburned organic vapors from a
geologic storage facility resulting from either equipment or containment failure.
(2)
[
(3)
[
§115.722.Site-wide Cap and Control Requirements.
(a)
The owner or operator of a site subject to this division
shall additionally comply with the requirements of Chapter 101, Subchapter
H, Division 6 of this title (relating to Highly-Reactive Volatile Organic
Compound Emissions Cap and Trade Program).
[
(b)
All sites subject to this division or
Division 2 of this subchapter (relating to Cooling Tower Heat Exchange Systems)
that are exempt from the highly-reactive volatile organic compound (HRVOC)
emissions cap and trade program, in accordance with §101.392 of this
title (relating to Exemptions), are limited to ten tons of HRVOC emissions
per calendar year.
(c)
Each site subject to this division is
subject to the following emission limitations.
(1)
HRVOC emissions at each site located in Harris County that
is subject to this division or Division 2 of this subchapter must not exceed
1,200 pounds of HRVOC per one-hour block period from any flare, vent, pressure
relief valve, cooling tower, or any combination.
(2)
HRVOC emissions at each site located in the Houston/Galveston
ozone nonattainment area as defined in §101.1 of this title (relating
to Definitions), excluding Harris County, that is subject to this division
or Division 2 of this subchapter must not exceed 1,200 pounds of HRVOC per
one-hour block period from any flare, vent, pressure relief valve, cooling
tower, or any combination.
(3)
For any exceedance of the HRVOC emission limits specified
in paragraph (1) or (2) of this subsection, the emission limits specified
in paragraph (1) or (2) of this subsection must be used to determine compliance
with subsection (a) or (b) of this section instead of the total amount of
actual emissions.
(d)
[
(1)
Average net heating value over a one-hour
block period will be used to demonstrate compliance with the minimum net heating
value requirements.
(2)
The exit velocity averaged over a one-hour
block period must be used to demonstrate compliance with the maximum exit
velocity requirements.
(e)
[
§115.725.Monitoring and Testing Requirements.
(a)
Except for pressure relief valves as defined in §115.10
of this title (relating to Definitions), each
[
(1)
For each uncontrolled vent subject to
the requirements of this subsection, the owner or operator shall:
(A)
select an operational parameter or parameters that directly
correlates to the HRVOC emissions from the vent;
(B)
install, calibrate, maintain, and operate according to
manufacturer's recommendations, a continuous monitoring system to monitor
and record the parameter or parameters selected under subparagraph (A) of
this paragraph; and
(C)
establish operating limits for the selected parameter or
parameters as the hourly average of the parameter or parameters during the
HRVOC emission test required under this subsection.
(2)
For each vent subject to the requirements
of this subsection that is controlled by a control device other than a flare,
the owner or operator shall:
(A)
select an operational parameter or parameters that directly
correlates to the HRVOC emissions directed to the control device;
(B)
select an operational parameter or parameters of the control
device that directly correlates to the control efficiency of the control device;
(C)
install, calibrate, maintain, and operate according to
manufacturer recommendations, continuous monitoring systems to monitor and
record the parameters selected under subparagraphs (A) and (B) of this paragraph;
and
(D)
establish operating limits for the selected parameters
required under subparagraphs (A) and (B) of this paragraph as the hourly averages
of the parameters during the HRVOC emission test required under this subsection.
(3)
To demonstrate compliance with the control
requirements of §115.722(a) - (c) of this title during emission events
and scheduled startup, shutdown, and maintenance activities, the owner or
operator shall determine the HRVOC emissions from each vent using one of the
following:
(A)
Testing using the appropriate reference methods and procedures
specified in this section; or
(B)
Process knowledge and engineering calculations. If process
knowledge and engineering calculations are used to determine HRVOC emissions
during emission events and scheduled startup, shutdown, and maintenance activities,
the monitoring plans required under paragraph (4) of this subsection must
also include all process information and calculations used to calculate the
HRVOC emissions.
(4)
The owner or operator shall develop, implement,
and follow a written monitoring plan for the continuous monitoring systems
required in paragraphs (1) and (2) of this subsection prior to performing
the monitoring and testing under this subsection. Upon written request by
the executive director, the monitoring plans shall be submitted within 30
days for review. The executive director may require additional or alternative
monitoring requirements. At a minimum, monitoring plans shall include:
(A)
specifications for all monitors used in the continuous
monitoring systems;
(B)
process and control device information supporting the selection
of parameters;
(C)
actual testing or manufacturer data documenting the control
efficiency of the control device; and
(D)
schedule of quarterly inspections of the continuous monitoring
systems to insure proper operation;
(5)
After the initial HRVOC emission test
required under this subsection, the owner or operator may perform additional
emission testing to update the data used to demonstrate compliance with the
control requirements of §115.722(a) - (c) of this title. Test plans for
additional testing must be submitted to the executive director at least 45
days prior to testing.
(6)
Testing using the appropriate reference
methods and procedures specified in §115.125 of this title that was conducted
before approval of the test plan required under §115.726(a) of this title
may be used in lieu of conducting the testing specified in this subsection,
provided that:
(A)
the owner or operator of the affected source obtains approval
for the testing report and data from the executive director; and
(B)
the testing establishes maximum potential HRVOC emissions
data expected during any operation that is not defined as an emissions event
or a scheduled maintenance, startup, or shutdown activity under §101.1
of this title.
(C)
if the monitoring system required under paragraphs (1)
or (2) of this subsection was not installed at the time of testing, the monitoring
plan required under paragraph (4) of this subsection must include sufficient
documentation to demonstrate that the monitoring system accurately reflects
the parameter operating limits established during testing. If the executive
director approves the prior testing under this paragraph, then the owner or
operator shall comply with the monitoring system and written monitoring plan
requirements of this subsection by no later than the compliance schedule in §115.729
of this title (relating to Counties and Compliance Schedules) instead of the
time required in paragraph (4) of this subsection.
(7)
The executive director may waive testing
for no more than one-half of the vents that are identical in design and operation
if the owner or operator demonstrates that all the vents are identical in
design and operation, and the emissions from all of the vents can be expected
to be identical.
(A)
The request for a waiver shall be submitted with the test
plan required under §115.726(a) of this title. Information required to
support the waiver request shall include, but is not limited to, the following:
(i)
identification of each vent expected to be identical;
(ii)
each specific vent to be tested;
(iii)
a detailed technical explanation demonstrating that the
measured emissions from the selected vents can be expected to be representative
of emissions from all vents;
(iv)
specific technical information for each vent and the process
associated with each vent demonstrating that the vents and associated processes
are identical in design and operation;
(v)
maintenance records for each vent and associated process
demonstrating the vents and associated processes have been maintained in a
similar manner; and
(vi)
any additional information or data requested by the executive
director necessary to demonstrate that the emissions from the vents can be
expected to be identical.
(B)
The executive director shall review the request for waiver
and may provide a temporary waiver authorizing testing of no more than one-half
of the vents. The results of the tests must be submitted to the executive
director no later than 45 days after the date of written authorization of
the temporary waiver. The executive director will determine if any further
testing is required based on the review of the test results.
(b)
The following alternatives may be used in lieu of
[
(1)
The vent gas stream may be equipped with a continuous emissions
monitoring system (CEMS), provided that:
(A)
(No change.)
(B)
the monitor shall initially and at a minimum
quarterly
[
(C)
(No change.)
(2)
Process knowledge, including scientific calculations and
other process monitoring data
sufficient to demonstrate compliance status
, may be used to determine maximum potential HRVOC hourly emission data.
Types of processes that may use process knowledge in lieu of testing are:
(A)
(No change.)
[(B)
pressure relief valves]
(B)
[
(C)
[
(D)
degassing safety devices, as defined in §115.720
of this title (relating to Applicability and Definitions).
(c)
Affected pressure relief valves not controlled
by a flare shall be monitored as follows:
(1)
Install, calibrate, maintain, and operate according to
manufacturer's recommendations, a continuous monitoring system on the pressure
relief valve or in the associated process systems sufficient to determine;
(A)
the time and duration of each pressure relief event;
(B)
the status of the pressure relief valve as either:
(i)
open or closed to the atmosphere; or
(ii)
the percentage the valve is open to the atmosphere; and
(C)
the volumetric flow rate during a pressure relief event.
(i)
If volumetric flow rate is not monitored directly, the
owner or operator must determine through engineering calculations, manufacturer's
information, or actual testing the correlation between the monitored parameter
and the percentage the pressure relief valve is open to the atmosphere to
the volumetric flow rate.
(ii)
If the monitoring system only indicates an open or closed
status as specified in subparagraph (B)(i) of this paragraph, the owner or
operator must assume the pressure relief valve is 100% open during a pressure
relief event for purposes of calculating volumetric flow rate.
(2)
For purposes of determining compliance with the control
requirement of §115.722(a) - (c) of this title during pressure relief
events, the owner or operator may use process knowledge, including scientific
calculations and other process monitoring data, to determine HRVOC emission
rates. The volumetric flow rate determined in accordance with paragraph (1)(C)
of this subsection shall be used in combination with the process knowledge
to determine HRVOC emission rates.
(3)
The owner or operator shall develop, implement, and follow
a written monitoring plan to satisfy the requirements of paragraphs (1) and
(2) of this subsection. The monitoring plan must include:
(A)
specifications for all monitors used to satisfy the requirements
of paragraphs (1) and (2) of this subsection;
(B)
all engineering calculations, manufacturer's information,
or actual testing supporting the correlation of the monitored parameters to
actual volumetric flow rate specified in paragraph (1)(C)(i) of this subsection;
(C)
supporting documentation of the actual testing or process
knowledge used to determine HRVOC emissions as provided in paragraph (2) of
this subsection;
(D)
at a minimum, quarterly inspections of all pressure relief
valves and associated monitors to insure proper operation per the manufacturer's
specifications; and
(E)
a list identifying all pressure relief valves in HRVOC
service subject to the requirements of this subsection);
(4)
Upon written request by the executive director, the monitoring
plan required under paragraph (3) of this subsection must be submitted within
30 days for review. The executive director may require additional or alternative
monitoring requirements.
[(c)
Testing using the appropriate reference
methods and procedures specified in §115.125 of this title which was
conducted before approval of the test plan required under §115.726(a)
of this title may be used in lieu of conducting the testing specified in subsection
(a) of this section, provided that:]
[(1)
the owner or operator of the affected source obtains approval
for the testing report and data from the executive director; and]
[(2)
the testing establishes maximum potential HRVOC emissions
data expected during any operation that is not defined as an emissions event
or a scheduled maintenance, startup, or shutdown activity under §101.1
of this title.]
(d)
Except as specified in
subsections (e) - (i)
[
(1)
install, calibrate, maintain, and operate a continuous
flow monitoring system capable of measuring the flow rate over the full potential
range of operation. The executive director may approve alternative means of
determining the flare flow rate for a period of time not to exceed 1.0% of
the annual operating time of the flare. The monitoring system
must
[
(A)
the temperature monitor
must
[
(B)
the pressure monitor
must
[
(C)
the flow monitor, or velocity monitor used to determine
flow rate,
must
[
(2)
install, calibrate, maintain, and operate an on-line analyzer
system capable of determining HRVOC at least once every 15 minutes. The on-line
analyzer system
must
[
(A)
Calibration of the on-line analyzer shall
be as follows:
(i)
for the HRVOC constituents,
follow
the procedures and requirements of Section 10.0 of 40 CFR Part 60, Appendix
B, Performance Specification 9, as amended through October 17, 2000 (65 FR
61744), except that the multi-point calibration procedure in Section 10.1
of Performance Specification 9
must
[
(ii)
for the constituents monitored to determine
of net heating value and molecular weight, the owner or operator may elect
to follow either the calibration procedures specified for HRVOC constituents
in clause (i) of this subparagraph or the calibration procedures recommended
by the analyzer manufacturer. If the owner or operator elects to follow manufacturer's
recommended procedures;
(I)
those calibration procedures must include, at a minimum,
single point calibration checks at least once every calendar week to meet
the acceptance criteria specified in Section 10.2 of Performance Specification
9 with certified standards of the top two non-HRVOC constituents affecting
molecular weight and net heating value, and,
(II)
the owner or operator shall submit with the quality assurance
plan (QAP) required under §115.726(a) of this title, manufacturer's information
and data to demonstrate the accuracy and reliability of the analyzer for those
monitored constituents for which routine calibration checks are not performed.
(iii)
the range of calibration standards for
the HRVOCs and other constituents may be based on the typical concentrations
observed rather than the full potential range of concentrations. Data must
be submitted with the QAP required under §115.726(a) of this title to
demonstrate the accuracy of the analyzer at maximum potential concentrations
outside of the proposed calibration range; and
(iv)
the executive director may specify additional
calibration requirements during approval of the QAP under §115.726(a)(1)(C)
of this title.
(B)
In lieu of monitoring constituents for
net heating value in accordance with this paragraph, the owner or operator
may install an online calorimeter to determine the net heating value. The
calorimeter must be calibrated, installed, operated, and maintained, in accordance
with manufacturer recommendations, to continuously measure and record the
net heating value of the gas sent to the flare, in British thermal units/standard
cubic foot of the gas.
(3)
continuously operate each monitoring system as required
by this section at least 95% of the time when the flare is operational, averaged
over a calendar year
. The percent measurement data availability must
be calculated as the total flare operating hours for which valid quality-assured
data was recorded divided by the total flare operating hours. Time required
for normal calibration checks required under paragraphs (1) and (2) of this
subsection is not considered downtime for purposes of this calculation.
[
(4)
during any period of monitor downtime of the on-line analyzer
specified in paragraph (2) of this subsection exceeding eight consecutive
hours, take a sample daily, starting within
ten
[
(5)
every 15 minutes, calculate the net heating value of the
gas combusted in the flare according to the equation given in 40 CFR §60.18(f)(3).
Pilot gas
must
[
(6)
calculate the actual exit velocity of
the flare every 15 minutes based on continuous flow rate, temperature, and
pressure monitor data, according to 40 CFR §60.18(f)(4); and
(7)
[
[(7)
calculate the actual exit velocity of
the flare every 15 minutes based on continuous flow rate, temperature, and
pressure monitor data, according to 40 CFR §60.18(f)(4). Average exit
velocity over an one-hour block period shall be used to demonstrate compliance
with the maximum exit velocity requirements of §115.722 (b) of this title;
and]
[(8)
submit for approval by the executive
director any minor modifications to these monitoring methods. Monitoring methods
other than those specified in paragraphs (1) and (2) of this subsection may
be used if approved by the executive director and validated by 40 CFR Part
63, Appendix A, Test Method 301 (December 29, 1992). For the purposes of this
paragraph, substitute "executive director" in each place that Test Method
301 references "administrator."]
(e)
Flares used solely for abatement of
HRVOC
emissions
from loading operations for
marine vessels or
transport vessels
[
[(1)
Flares used solely for abatement of emissions
from loading operations for transport vessels shall satisfy all of the following
requirements.]
(1)
[
[(B)
Records of each loading activity are
maintained, including, but not limited to:]
[(i)
the type of vessel being loaded;]
[(ii)
the start time and the end time for each vessel loaded;]
[(iii)
the compounds loaded, in addition to the compounds loaded
into the vessel immediately previous to the current loading operation, if
the vessel being loaded is not clean;]
[(iv)
the quantity of material loaded;]
[(v)
the loading rate in gallons per minute;]
[(vi)
the method of loading, such as submerged fill, bottom
fill, or splash loading; and]
[(vii)
additional parameters as needed for emissions calculations.]
(2)
[
(3)
[
(4)
For flares that receive greater than 98%
of an individual HRVOC at all times, the owner or operator may use process
knowledge to determine net heating value and HRVOC concentration for demonstrating
compliance with §115.722(a) - (d) of this title.
[(2)
Temporary portable flares used solely
for abatement of emissions from scheduled maintenance or startup or shutdown
activities shall satisfy all of the following requirements.]
[(A)
The flare is designed to be and capable of being carried
or moved from one location to another by means including, but not limited
to, wheels, skids, dolly, trailer, or platform.]
[(B)
The flare shall be located and operated for no more than
14 days at the plant site in any 12 consecutive months.]
[(C)
A calorimeter shall be calibrated, installed, operated,
and maintained, in accordance with manufacturer recommendations, to continuously
measure and record the net heating value of the gas sent to the flare, in
British thermal units per standard cubic foot of the gas.]
[(D)
Records shall be maintained, including, but not limited
to:]
[(i)
the date, start time, and end time for each flaring event;]
[(ii)
the flow rate of the gas routed to the flare, in standard
cubic feet per minute, calculated based on process knowledge or actual measurement;
and]
[(iii)
all supporting supplemental information on which the
flow rate calculation was based.]
[(E)
The flare's actual exit velocity for each activity shall
be calculated every 15 minutes, based on the calculated flow rate and the
supplemental fuel rate corrected to standard temperature and pressure and
the unobstructed (free) cross-sectional area of the flare tip, according to
40 CFR §60.18(f)(4).]
(f)
Flares used solely for abatement of emissions
from scheduled maintenance, startup, or shutdown activities must comply with
the continuous monitoring requirements in subsection (d) of this section,
or satisfy all of the following requirements:
(1)
A single flare must not be operated in HRVOC service for
more than 14 days at an account in any 12 consecutive months.
(2)
The total number of days for which an account may send
HRVOCs temporarily to multiple flares as described in this subsection must
not exceed 28 days in 12 consecutive months.
(3)
To demonstrate compliance with the minimum net heating
value requirements of §115.722(d) of this title, a calorimeter must be
calibrated, installed, operated, and maintained, in accordance with manufacturer
recommendations, to continuously measure and record the net heating value
of the gas sent to the flare, in British thermal units per standard cubic
foot of the gas.
(4)
The flow rate of the gas routed to the flare, in standard
cubic feet per minute must be determined by either:
(A)
complying with the monitoring requirements of subsection
(d)(1) of this section, or
(B)
using process knowledge and engineering calculations.
(5)
The flare's actual exit velocity for each activity must
be calculated on a block 15-minute average basis, corrected to standard temperature
and pressure and the unobstructed (free) cross-sectional area of the flare
tip, according to 40 CFR §60.18(f)(4). The HRVOC hourly average mass
emission rates from the flare must be calculated to demonstrate compliance
with §115.722(a) - (c) of this title, using total HRVOC sent to the flare
calculated based on process knowledge or actual measurement, assuming a 99%
destruction efficiency for ethylene and propylene and a 98% destruction efficiency
for all other HRVOCs when the flare meets the net heating value and exit velocity
requirements of 40 CFR §60.18. During each 15-minute period when the
flare does not meet the net heating value or exit velocity requirements of
40 CFR §60.18, a destruction efficiency of 93% must be assumed to calculate
HRVOC mass emission rates.
(6)
For flares that at all times receive greater than 98% of
an individual HRVOC, the owner or operator may use process knowledge to determine
net heating value and HRVOC concentration for demonstrating compliance with §115.722(a)
- (d) of this title.
(g)
For an emergency flare, as defined in §115.10
of this title, subject to the requirements of this division, the owner or
operator shall:
(1)
comply with the continuous monitoring requirements in subsection
(d) of this section, or;
(2)
use process knowledge and engineering calculations to determine
compliance with the requirements of §115.722(a) - (d) of this title during
an upset event or unscheduled maintenance, startup, or shutdown activity.
If this option is selected the owner or operator shall comply with the following:
(A)
for emergency flares equipped with physical seal (e.g.,
a water seal) that prevents emissions from being sent to the flare except
during an upset event or unscheduled maintenance, startup, or shutdown activity,
the owner or operator shall install, calibrate, operate, and maintain, according
to manufacturer's specifications, a continuous monitoring system that:
(i)
monitors the status of the physical seal to ensure that
emissions are not directed to the flare except during an upset event or unscheduled
maintenance, startup, or shutdown activity;
(ii)
automatically records the time and duration of each event
when emissions are sent to the flare; and
(iii)
verifies that the physical seal has been restored after
each event;
(B)
for emergency flares not equipped with a physical seal
that prevents emissions from being sent to the flare except during an upset
event or unscheduled maintenance, startup, or shutdown activity, the owner
or operator shall;
(i)
install, calibrate, operate, and maintain, according to
manufacturers' specifications, a flow monitoring or indicating system to determine
and record the time and duration of each event when emissions are sent to
the flare; and
(ii)
determine through process knowledge, engineering calculations,
or actual testing, the baseline flow rate from any purge/sweep gas and the
minimum flow rate indicative of an upset event or unscheduled maintenance,
startup, or shutdown activity;
(C)
the owner or operator shall develop, implement, and follow
a written monitoring plan to satisfy the requirements of subparagraph (A)
or (B) of this paragraph. The monitoring plan must include:
(i)
specifications for all monitors used to satisfy the requirements
of subparagraph (A) or (B) of this paragraph;
(ii)
the engineering calculations and process information used
to determine volumetric flow rate, flare tip exit velocity, net heating value,
HRVOC emissions for compliance with §115.722(a) - (d) of this title;
and
(iii)
at a minimum, quarterly inspections of the continuous
monitoring system to ensure proper operation.
(D)
Upon written request by the executive director, the monitoring
plans required in accordance with subparagraph (C) of this paragraph shall
be submitted within 30 days for review. The executive director may require
additional or alternative monitoring requirements.
(E)
The flare's actual exit velocity for each activity must
be calculated on a block 15-minute average basis, corrected to standard temperature
and pressure and the unobstructed (free) cross-sectional area of the flare
tip, according to 40 CFR §60.18(f)(4). The HRVOC hourly average mass
emission rates from the flare must be calculated, using total HRVOC sent to
the flare calculated based on process knowledge or actual measurement, assuming
a 99% destruction efficiency for ethylene and propylene and a 98% destruction
efficiency for all other HRVOCs when the flare meets the net heating value
and exit velocity requirements of 40 CFR §60.18. During each 15-minute
period when the flare does not meet the net heating value or exit velocity
requirements of 40 CFR §60.18, a destruction efficiency of 93% must be
assumed to calculate HRVOC mass emission rates.
(h)
Flares other than emergency flares that
temporarily receive HRVOC emissions during any operation that is not a scheduled
maintenance, startup, or shutdown activity as defined in §101.1 of this
title must satisfy the following requirements:
(1)
The flare must not be operated in HRVOC service for more
than 14 days at the plant site in any 12 consecutive months.
(2)
The total number of days for which an account may send
HRVOCs temporarily to multiple flares as described in this subsection must
not exceed 28 days in 12 consecutive months.
(3)
In lieu of the flow monitoring requirements of subsection
(d)(1) of this section, the owner or operator may use one of the following
to demonstrate compliance with §115.722(a) - (d) of this title:
(A)
process knowledge;
(B)
actual measurement; or
(C)
for flares that temporarily receive HRVOC emissions from
flare systems that are monitored in accordance with subsection (d) of this
section, the flow monitoring data from the monitored flare system may be used
as data substitution. Maximum flow rate, excluding data from startups, shutdowns,
maintenance, or emissions events, from the previous 30 operational days must
be used to determine compliance with §115.722(a) - (d) of this title.
(4)
In lieu of implementing the continuous monitoring requirements
specified in subsection (d)(2) of this section, the owner operator may use
one of the following to demonstrate compliance with §115.722(a) - (d)
of this title:
(A)
for all flares in temporary HRVOC service, daily sampling
in accordance with subsection (d)(4) of this section to determine net heating
value and HRVOC concentrations; or
(B)
for flares that temporarily receive HRVOC emissions for
less than 72 consecutive hours from flare systems that are monitored in accordance
with subsection (d) of this section, the monitoring data from the monitored
flare system may be used as data substitution to satisfy compliance with §115.722(a)
- (d) of this title. Maximum HRVOC concentrations and minimum net heating
value, excluding data from scheduled startups, shutdowns, maintenance, or
emissions events, from the previous 30 operational days shall be used to determine
compliance with §115.722(a) - (d) of this title.
(5)
If an emissions event as defined in §101.1 of this
title occurs while HRVOC emissions are being routed to a flare temporarily
under this subsection, the owner or operator shall demonstrate compliance
with the requirements of §115.722(a) - (d) of this title using process
knowledge and engineering calculations in accordance with subsection (g)(2)(E)
of this section.
(i)
For flares specifically designed to receive
and control liquid or dual phase streams containing HRVOCs, process knowledge
and engineering calculations must be used to determine compliance with the
requirements of §115.722(a) - (d) of this title in accordance with subsection
(g)(2)(E) of this section.
(j)
[
(k)
Upon written request by the executive
director, the owner or operator shall submit the engineering calculations
and process information used to determine volumetric flow rate, flare tip
exit velocity, net heating value, and HRVOC emissions for compliance with
the requirements of §115.722(a) - (d) of this title where applicable
under the requirements of this section. The information must be submitted
within 30 days for review.
[(g)
The executive director may waive testing
for no more than one-half of the vents that are identical in design and operation
if the owner or operator demonstrates that all the vents are identical in
design and operation, and the emissions from all of the vents can be expected
to be identical.]
[(1)
The request for a waiver shall be submitted with the test
plan required under §115.726(a)(2) of this title. Information required
to support the waiver request shall include, but is not limited to, the following:]
[(A)
identification of each vent expected to be identical;]
[(B)
each specific vent to be tested;]
[(C)
a detailed technical explanation demonstrating that the
measured emissions from the selected vents can be expected to be representative
of emissions from all vents;]
[(D)
specific technical information for each vent and the process
associated with each vent demonstrating that the vents and associated processes
are identical in design and operation;]
[(E)
maintenance records for each vent and associated process
demonstrating the vents and associated processes have been maintained in a
similar manner; and]
[(F)
any additional information or data requested by the executive
director necessary to demonstrate that the emissions from the vents can be
expected to be identical.]
[(2)
The executive director shall review the request for waiver
and may provide a temporary waiver authorizing testing of no more than one-half
of the vents. The results of the tests shall be submitted to the executive
director no later than 45 days after the date of written authorization of
the temporary waiver. The executive director will determine if any further
testing is required based on the review of the test results.]
§115.726.Recordkeeping and Reporting Requirements.
(a)
To satisfy the requirements of §115.725 of this title
(relating to Monitoring and Testing Requirements), the owner or operator of
each affected flare or vent gas stream shall submit to the executive director
for [
(1)
for
the
monitoring
requirements of §115.725(d)
of this title
:
(A)
for flares and vent gas streams existing on or before December
31, 2005,
the QAP must be submitted
no later than April 30, 2005;
(B)
for flares/vent gas streams that become subject to the
requirements of this division after December 31, 2005,
the QAP must be
submitted prior to the flares or vent gas streams being placed in a highly-reactive
organic compound (HRVOC) service
[
(C)
(No change.)
(2)
for
the
testing
requirements of §115.725(a)
of this title
:
(A)
for flares and vent gas streams existing on or before December
31, 2005,
the test plan must be submitted
no later than April 30,
2005;
(B)
for flares and vent gas streams that become subject to
the requirements of this division after December 31, 2005,
the test plan
must be submitted
at least 60 days prior to being placed in HRVOC service;
[
(C)
the executive director shall issue written approval of,
or detail deficiencies and/or direct additional requirements to be added to,
each test plan within 45 days of receipt of a test plan for a vent gas stream
to be tested as required by §115.725(a) of this title. The owner or operator
shall submit a corrected test plan within 45 days of the date of the deficiency
and/or additional requirements letter. If an approval or detailed deficiency
and/or directed additional requirements letter is not issued within 45 days
of receipt by the executive director, then the test plan is approved by default
provided the testing is to be conducted in accordance with the appropriate
reference methods and procedures specified in §115.125 of this title
(relating to Testing Requirements) without deviation
; and
[
(D)
The operational parameters selected in
accordance with §115.725(a)(1)(A) and (2)(A) and (B) of this title must
be identified in the test plan.
(b)
The owner or operator
of a vent gas stream subject
to the requirements of §115.725(a) of this title
shall
comply
with the following recordkeeping requirements as applicable:
[
(1)
maintain records of all testing conducted
in accordance with §115.725(a) of this title to determine HRVOC emission
rates on a pounds-per-hour basis for each affected vent gas stream;
(2)
maintain hourly records of the parameter
monitoring in accordance with §115.725(a)(1) or (2) of this title;
(3)
maintain records of the monitoring plans
required under §115.725(a)(4) of this title;
(4)
maintain hourly records of HRVOC emission
rates on a pound-per-hour basis for each affected vent gas stream monitored
in accordance with §115.725(b)(1) of this title;
(5)
maintain records of all continuous emissions
monitoring system calibrations and cylinder gas audits performed in accordance
with §115.725(b)(1)(A) and (B) of this title;
(6)
maintain records of all process information
and calculations used to determine vent gas flow rate as specified in §115.725(b)(1)(C)
of this title; and
(7)
maintain records of all process information,
actual testing, process monitoring data, and calculations used to comply with §115.725(a)
of this title under the alternatives to the testing requirements in §115.725(b)(2)
of this title;
(c)
The owner or operator of a pressure relief
valve subject to the requirements of §115.725(c) of this title shall
comply with the following recordkeeping requirements:
(1)
maintain records of the date, time, duration, volumetric
flow rate, and speciated and total HRVOC emission rates on a pounds-per-hour
basis for each pressure relief event;
(2)
maintain hourly records of the parameter monitoring in
accordance with §115.725(c)(1) of this title;
(3)
maintain records of all process information, monitored
data, and calculations used to determine volumetric flow rate and HRVOC hourly
emission data as specified in §115.725(c)(2) of this title; and
(4)
maintain records of the monitoring plans required under §115.725(c)(3)
of this title.
(d)
[
(1)
maintain hourly records of the speciated and total HRVOC
emission rates on a pounds-per-hour basis for each affected flare in order
to demonstrate compliance with §115.722 of this title;
(2)
maintain records of all monitoring, testing, and calibrations
performed in accordance with the provisions of §115.725 of this title;
(3)
maintain records on a weekly basis that detail all corrective
actions made to the continuous monitoring systems during monitor downtimes,
and any delay in corrective action[
(4)
maintain records of each
15-minute average
calculated
net heating value of the gas stream routed to the flare and each
15-minute
average
calculated exit velocity at the flare tip, determined in accordance
with the provisions of §115.725 of this title
; and
[
(5)
for flares subject to the monitoring requirements
of §115.725(e) of this title, maintain records of each loading activity
including, but not limited to:
(A)
the size of vessel being loaded;
(B)
the start time and the end time for each vessel loaded;
(C)
the compounds loaded, in addition to the compounds loaded
into the vessel immediately previous to the current loading operation, if
the vessel being loaded is not clean;
(D)
the quantity of material loaded;
(E)
the loading rate in gallons per minute;
(F)
the method of loading, such as submerged fill, bottom fill,
or splash loading; and
(G)
all process information, monitored data, and calculations
used to determine volumetric flow rate and HRVOC hourly emission data.
(6)
for flares used solely for the abatement
of emissions from scheduled maintenance, startup, or shutdown activities in §115.725(f)
of this title, the owner or operator shall maintain records, including, but
not limited to:
(A)
the date, time, and duration for each flaring event;
(B)
the flow rate of the gas routed to the flare, in standard
cubic feet per minute; and
(C)
all process information, monitored data, and calculations
used to determine volumetric flow rate and HRVOC hourly emission data.
(7)
for emergency flares subject to the requirements
of §115.725(g) of this title, maintain records including, but not limited
to:
(A)
the date, time, and duration for each flaring event;
(B)
the volumetric flow rate of the gas routed to the flare,
in standard cubic feet per minute;
(C)
all process information, monitored data, and calculations
used to determine net heating value, volumetric flow rate, and HRVOC hourly
emission data.
(D)
hourly records of the parameter monitoring in accordance
with §115.725(g)(2)(A) or (B) of this title; and
(E)
records of the monitoring plans required under §115.725(g)(2)(C)
of this title;
(8)
for flares subject to the requirements
of §115.725(h) or (i) of this title, maintain records including, but
not limited to:
(A)
the date, time, and duration for each flaring event;
(B)
the volumetric flow rate of the gas routed to the flare,
in standard cubic feet per minute; and
(C)
all process information, monitored data, and calculations
used to determine net heating value, volumetric flow rate, and HRVOC hourly
emission data.
(e)
[
(1)
The owner or operator of any account claiming exemption
under §115.727(a) of this title [
(2)
The owner or operator of any flare claiming exemption under §115.727(b)
of this title shall maintain records
that
[
(3)
The owner or operator of any vent gas stream or flare claiming
exemption under §115.727 of this title shall comply with the following
recordkeeping requirements:
(A)
for vent gas streams, maintain records
that
[
(B)
for flares, maintain records
that
[
(f)
The owner or operator claiming an exemption
under §115.727(e) of this title shall submit written notification to
the executive director at least 15 days prior to permanently removing a flare
from service, but no later than December 31, 2005.
(g)
[
(1)
cooling tower emissions from cooling towers
that
[
(2)
all
emissions from flares, vents, and pressure relief
valves subject to the requirements of §115.725 of this title.
[
[(3)
the maximum potential emission rate from
vent gas streams and flares which are not continuously monitored.]
(h)
The owner or operator of each account
subject to §115.722 of this title shall maintain hourly records to demonstrate
compliance with the one-hour block emissions limits specified in §115.722(c)
of this title, including:
(1)
cooling tower emissions from cooling towers that are subject
to Division 2 of this subchapter; and
(2)
all emissions from flares, vents, and pressure relief valves
subject to the requirements of §115.725 of this title.
(i)
[
§115.727.Exemptions.
(a)
Any account for which all individual gas streams routed
to a flare contain less than 5.0% by weight of highly-reactive volatile organic
compounds
HRVOCs
[
(b)
For a flare that at no time receives a gas stream containing
5.0% or greater
HRVOCs
[
(1)
the gas stream directed to the flare shall be treated as
a vent gas stream for purposes of determining compliance with
§115.722(a)
- (c)
[
(2)
the flare is exempt from the continuous monitoring requirements
of
§115.726(d)
[
[(c)
Emissions from scheduled maintenance,
startup, or shutdown activities in compliance with §101.211 of this title
(relating to Scheduled Maintenance, Startup, and Shutdown Reporting and Recordkeeping
Requirements) are exempt from the requirements of §115.722(a) of this
title.]
[(d)
Emissions from emissions events in compliance
with §101.201 of this title (relating to Emissions Event Reporting and
Recordkeeping Requirements) are exempt from the requirements of §115.722(a)
of this title.]
(c)
[
(1)
A vent gas stream that has no potential to emit
HRVOCs
[
(2)
A vent gas stream that has the potential to emit
HRVOCs
[
(3)
Vent gas streams from the following sources are exempt
from the requirements of this division with the exception of the recordkeeping
requirements of
§115.726(e)(3)(A)
[
(A)
vent gas streams resulting from the combustion of less
than 5.0%
by weight
HRVOC in boilers, furnaces, engines, turbines,
incinerators,
and heaters;
(B)
pressure tanks
that
[
(C)
laboratory vent hoods;
(D)
instrumentation air systems;
(E)
atmospheric storage tanks;
(F)
wastewater system vents;
(G)
cooling towers; and
(H)
equipment leak fugitive components, except for vents from
pressure relief valves occurring when the process pressure is sufficient to
overcome the preset pressure relief point of the pressure relief valve and
emissions are either released directly to the atmosphere or routed to a control
device.
(d)
[
(e)
Any flare that will be permanently out
of service by April 1, 2006 is exempt from the requirements of this division,
with the exception of the recordkeeping requirements in §115.726(f) of
this title.
§115.729.Counties and Compliance Schedules.
Each owner or operator in Brazoria, Chambers, Fort Bend, Galveston,
Harris, Liberty, Montgomery, and Waller Counties shall demonstrate compliance
with the requirements of this division (relating to Vent Gas Control) in accordance
with the following schedule.
(1)
Vent gas
and pressure relief valves
.
(A)
The testing
and monitoring
required by §115.725
of this title (relating to Monitoring and Testing Requirements)
must
[
(B)
The owner or operator shall demonstrate compliance with
all other requirements of this division applicable to vent gas streams
and pressure relief valves as
soon as practicable, but no later than
April 1, 2006.
(2)
Flares. The owner or operator of each flare shall demonstrate
compliance with all sections of this division as soon as practicable, but
no later than December 31, 2005, with the exception of
§115.722(a)
- (c)
[
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 June 25, 2004.
TRD-200404256
Stephanie Bergeron
Director, Environmental Law Division
Texas Commission on Environmental Quality
Earliest possible date of adoption: August 8, 2004
For further information, please call: (512) 239-6087
30 TAC §§115.760, 115.761, 115.764, 115.766, 115.767, 115.769
STATUTORY AUTHORITY
The amendments and new sections are proposed under Texas Water Code, §5.103,
concerning Rules, and §5.105, concerning General Policy, that authorize
the commission to adopt rules necessary to carry out its powers and duties
under the Texas Water Code; and under Texas Health and Safety Code, §382.017,
concerning Rules, that authorizes the commission to adopt rules consistent
with the policy and purposes of the Texas Clean Air Act. The amendments and
new sections are also proposed under Texas Health and Safety Code, §382.002,
concerning Policy and Purpose, that establishes the commission's purpose to
safeguard the state's air resources, consistent with the protection of public
health, general welfare, and physical property; §382.011, concerning
General Powers and Duties, that authorizes the commission to control the quality
of the state's air; §382.012, concerning State Air Control Plan, that
authorizes the commission to prepare and develop a general, comprehensive
plan for the proper control of the state's air; and §382.016, concerning
Monitoring Requirements Examination of Records, that authorizes the commission
to prescribe reasonable requirements for measuring and monitoring the emissions
of air contaminants.
The proposed amendments and new sections implement Texas Health and Safety
Code, §§382.002, 382.011, 382.012, and 382.017.
§115.760.Applicability and Cooling Tower Heat Exchange System Definitions.
(a)
Applicability. Any account with a cooling tower heat exchange
system in the Houston/Galveston area, as defined in §115.10 of this title
(relating to Definitions),
that
[
(b)
Definitions. The following term, when used in this division,
[
§115.761.Site-wide Cap.
(a)
The owner or operator of a site subject to this division
shall additionally comply with the requirements of Chapter 101, Subchapter
H, Division 6 of this title (relating to Highly-Reactive Volatile Organic
Compound Emissions Cap and Trade Program).
[
(b)
All sites subject to this division or
Division 1 of this subchapter (relating to Vent Gas Control) that are exempt
from the highly-reactive volatile organic compound (HRVOC) emissions cap and
trade program, in accordance with §101.392 of this title (relating to
Exemptions), are limited to ten tons of HRVOC emissions per calendar year.
(c)
Each site subject to this division is
subject to the following emission limitations:
(1)
HRVOC emissions at each site located in Harris County that
is subject to this division or Division 1 of this subchapter (relating to
Vent Gas Control) must not exceed 1,200 pounds of HRVOCs per one-hour block
period from any flare, vent, pressure relief valve, cooling tower, or any
combination.
(2)
HRVOC emissions at each site located in the Houston/Galveston
ozone nonattainment area as defined in §101.1 of this title (relating
to Definitions), excluding Harris County, that is subject to this division
or Division 1 of this subchapter must not exceed 1,200 pounds of HRVOCs per
one-hour block period from any flare, vent, pressure relief valve, cooling
tower, or any combination.
(3)
For any exceedance of the HRVOC emission limits specified
in paragraph (1) or (2) of this subsection, the emission limits specified
in paragraph (1) or (2) of this subsection must be used to determine compliance
with subsection (a) or (b) of this section instead of the total amount of
actual emissions.
(d)
[
§115.764.Monitoring and Testing Requirements.
(a)
The owner or operator of a cooling tower heat exchange
system with [
(1)
(No change.)
(2)
install, calibrate, operate, and maintain a system to continuously
determine the total strippable volatile organic compound (VOC) concentration
at each inlet of each cooling tower.
The continuous monitor must be calibrated
with methane or a VOC that best represents potential leakage into the cooling
tower system and the emissions from the system. Calibration must be checked
weekly or more frequently, as necessary, to maintain a monitor drift of less
than 5.0%.
During out-of-order periods of the VOC monitor(s), a sample
must
[
(3)
continuously operate each monitoring system as required
by this section at least 95% of the time when the cooling tower is operational,
averaged over a calendar year
. The percent measurement data availability
must be calculated as the total operating hours of the cooling tower heat
exchange system for which valid quality-assured data was recorded divided
by the total operating hours of the cooling tower heat exchange system. Time
required for normal calibration checks required under this subsection is not
considered downtime for purposes of this calculation
;
(4)
determine the speciated strippable
highly-reactive
volatile organic compound (HRVOC)
[
(5)
if the concentration of total strippable VOC is equal to
or greater than 50 parts per billion by weight (ppbw) in the cooling tower
water for more than a one-hour block of time, collect an additional sample
to determine speciated and total HRVOC in accordance with
the air-stripping
method in Appendix P
[
(6)
in lieu of the monitoring in paragraph (2) of this subsection
and the sampling for speciation of strippable
HRVOC
[
(b)
The owner or operator of a cooling tower heat exchange
system with [
(1)
install, calibrate, operate, and maintain a continuous
flow monitor on each inlet of each cooling tower. Each monitor
must
[
(2)
determine the total strippable VOC concentration by collecting
samples from each inlet of each cooling tower at least twice per week in accordance
with
the air-stripping method in Appendix P
[
(3)
operate
each monitoring system [
(4)
determine the speciated strippable HRVOC concentration
by collecting samples from each inlet of each cooling tower at least once
per month in accordance with
the air-stripping method in Appendix P
[
(5)
if the
concentration of
[
(6)
in lieu of the monitoring in paragraph (2) of this subsection
and the sampling for speciation of strippable
HRVOC
[
(c)
When periodic sampling is required, the
[
[(d)
The owner or operator of an affected
cooling tower heat exchange system shall submit for review and approval by
the executive director a quality assurance plan (QAP) for the installation,
calibration, operation, and maintenance for the monitoring equipment required
by this division as follows:]
[(1)
for cooling towers existing on or before December 31,
2005, no later than April 30, 2005;]
[(2)
for cooling tower heat exchange systems that become subject
to the requirements of this division after December 31, 2005, at least 60
days prior to being placed in service. This plan shall be submitted prior
to initiating a monitoring program to comply with the requirements of subsections
(a) and (b) of this section. Additionally, the plan must define each compound
which could potentially leak through the heat exchanger and therefore directly
impact the emissions of the cooling water system; and]
[(3)
the executive director shall issue written approval of,
or detail deficiencies and/or direct additional requirements to be added to,
each QAP within 180 days of receipt of a complete QAP that details the owner
or operator's plans for installation, calibration, operation, and maintenance
of the cooling tower heat exchange system monitoring. The owner or operator
shall submit a corrected QAP within 60 days of the date of the deficiency
and/or additional requirements letter. If an approval or detailed deficiency
and/or directed additional requirements letter is not issued within 180 days
of receipt by the executive director, then the QAP is approved by default.]
(d)
[
(e)
[
(1)
use the maximum potential flow rate based on manufacturer's
pump performance data, assuming no back pressure; or
(2)
install, calibrate, operate, and maintain, in accordance
with the manufacturer's recommendations, a monitor to continuously measure
and record each cooling water pump discharge pressure to establish the total
dynamic head of the cooling water system. The owner or operator of the cooling
water system must establish, use, and demonstrate in the QAP required in
§115.766(i) of this title (relating to Recordkeeping and Reporting Requirements
[
(f)
[
(g)
In lieu of using the monitor location
described in subsections (a) and (b) of this section, the owner or operator
of cooling tower heat exchange systems in which a single cooling tower services
both HRVOC and non-HRVOC process units may:
(1)
install a flow monitor, meeting the requirements of subsections
(a)(1) and (b)(1) of this section at a point that represents the flow of cooling
water from only the HRVOC-containing process units; and
(2)
monitor the total strippable VOC or HRVOC concentration,
in accordance with subsection (a), (b), or (d) of this section at a point
leaving the HRVOC-containing process unit and prior to mixing with cooling
tower water from other units.
§115.766.Recordkeeping and Reporting Requirements.
(a)
The owner or operator of any cooling tower heat exchange
system subject to §115.761 of this title (relating to Site-wide Cap)
shall comply with the following recordkeeping requirements:
(1)
establish and maintain a process diagram of the cooling
tower heat exchange system, including the locations at which the system will
be monitored and sampled such that the cooling water is not exposed to the
atmosphere prior to sampling;
(2)
maintain records of all monitoring, testing, and calibrations
performed in accordance with the provisions of §115.764 of this title
(relating to Monitoring and Testing Requirements);
(3)
maintain hourly records that document the emission rate
in pounds per hour (lb/hr) for each hour for speciated highly-reactive volatile
organic compounds (HRVOC) and total HRVOC from the cooling water for each
cooling tower heat exchange system as required by §115.764(a), (b), or
(d) of this title. The flow rate of the cooling water in conjunction with
the most recently monitored concentration of the speciated HRVOC or total
HRVOC in the cooling tower water, shall be used to calculate the respective
emission rate in lb/hr. If the concentration results of the speciated HRVOC
or total HRVOC analyses are below the minimum detection limit (i.e., non-detected),
then half the detection limit(s) must be used to calculate HRVOC emissions;
(4)
maintain hourly records of the total strippable VOC concentration
in the cooling water for cooling tower heat exchanger systems monitored in
accordance with §115.764(a)(2) of this title, and maintain records of
each test for total strippable VOC concentration performed in accordance with §115.764(b)(2)
or (d) of this title. If the concentrations results of the total strippable
VOC testing or monitoring are below the minimum detection limit, then the
full detection limit must be used to calculate average total strippable VOC
concentration;
(5)
maintain hourly records of the cooling water flow rate;
and
(6)
maintain records on a weekly basis that detail all corrective
actions and any delay in corrective action taken by documenting the dates,
reasons, and durations of such occurrences and the estimated quantity of all
HRVOC emissions during such activities;
(b)
The owner or operator of any cooling tower heat exchange
system claiming an exemption under §115.767 of this title (relating to
Exemptions) shall comply with the following recordkeeping requirements:
(1)
maintain records of the heat exchanger pressure differential
to document continuous compliance with the exemption criteria of §115.767(1)
of this title; or
(2)
maintain records of the content of the process side fluid
in each heat exchanger to demonstrate continuous compliance with the exemption
criteria of §115.767(2) of this title.
(c)
The owner or operator shall maintain all records necessary
to demonstrate continuous compliance and records of periodic measurements
for at least five years and make them available for review upon request by
authorized representatives of the executive director, United States Environmental
Protection Agency, or any local air pollution control agency with jurisdiction.
(d)
The owner or operator of any cooling tower heat exchange
system using the alternate periodic monitoring available under §115.764(d)
of this title shall maintain sufficient records to demonstrate that no individual
heat exchanger has 5.0% or greater HRVOC in the process-side fluid.
(e)
The owner or operator of any cooling tower heat exchange
system using manufacturer's pump performance data to determine the maximum
potential flow rate, as specified in §115.764(e)(1) of this title, shall
maintain the following records for each pump:
(1)
the manufacturer's certified pump performance test;
(2)
the operating status of each pump;
(3)
the motor manufacturer, model number, and rated brake horsepower;
(4)
the impeller manufacturer, model number, size, and design;
(5)
any change to a cooling tower heat exchange system pump
or pumping system in which the change would modify the basis for design pumping
capacity; and
(6)
the effect of any change on the maximum potential flow
rate.
(f)
The owner or operator of any cooling tower heat exchange
system using a system to monitor cooling water pump discharge pressure to
determine the continuous flow rate for each cooling tower, as specified in §115.764(e)(2)
of this title, shall maintain the following records for each pump:
(1)
the continuous measurement of cooling water pump discharge
pressure;
(2)
the manufacturer's certified pump performance test;
(3)
the operating status of each pump;
(4)
the motor manufacturer, model number, and rated brake horsepower;
(5)
the impeller manufacturer, model number, size, and design;
(6)
any change to a cooling tower heat exchange system pump
or pumping system in which the change would modify the basis for design pumping
capacity; and
(7)
the effect of any change on the maximum potential flow
rate.
(g)
The owner or operator of each account subject to §115.761
of this title shall maintain daily records to demonstrate compliance with
the tons per calendar year emissions limits specified in §115.761(a)
and (b) of this title, including:
(1)
flare, vent gas, and pressure relief valve emissions that
are subject to Division 1 of this subchapter (relating to Vent Gas Control);
and
(2)
all cooling towers subject to the requirements of §115.764
of this title.
(h)
The owner or operator of each account subject to §115.761
of this title shall maintain hourly records to demonstrate compliance with
the one-hour block emissions limits specified in §115.761(c) of this
title, including:
(1)
flare, vent gas, and pressure relief valve emissions that
are subject to Division 1 of this subchapter; and
(2)
all cooling towers subject to the requirements of §115.764
of this title.
(i)
The owner or operator of an affected cooling tower heat
exchange system shall submit for review and approval by the executive director
a quality assurance plan (QAP) for the installation, calibration, operation,
and maintenance for the monitoring equipment required by this division as
follows:
(1)
for cooling towers existing on or before December 31, 2005,
the QAP must be submitted no later than April 30, 2005;
(2)
for cooling tower heat exchange systems that become subject
to the requirements of this division after December 31, 2005, the QAP must
be submitted prior to being placed in HRVOC service; and
(3)
the executive director shall issue written approval of,
or detail deficiencies and/or direct additional requirements to be added to,
each QAP within 180 days of receipt of a complete QAP that details the owner
or operator's plans for installation, calibration, operation, and maintenance
of the cooling tower heat exchange system monitoring. The owner or operator
shall submit a corrected QAP within 60 days of the date of the deficiency
and/or additional requirements letter. If an approval or detailed deficiency
and/or directed additional requirements letter is not issued within 180 days
of receipt by the executive director, then the QAP is approved by default.
(j)
The owner or operator claiming an exemption under §115.767(4)
of this title shall submit written notification to the executive director
at least 15 days prior to permanently removing a cooling tower heat exchange
system from service, but not later than December 31, 2005.
§115.767.Exemptions.
The following exemptions apply.
(1)
Any cooling tower heat exchange system in which each individual
heat exchanger with greater than 100 parts per million by weight (ppmw) highly-reactive
volatile organic compounds (HRVOC) in the process side fluid is operated with
the minimum pressure on the cooling water side at least five pounds per square
inch, gauge (psig) greater than the maximum pressure on the process side,
as demonstrated by continuous pressure monitoring and recording at all heat
exchangers with greater than 100 ppmw HRVOC in the process side fluid, is
exempt from the requirements of this division (relating to Cooling Tower Heat
Exchange Systems), with the exception of the recordkeeping requirements of §115.766(b)
and (c) of this title (relating to Recordkeeping and Reporting Requirements).
(2)
Any cooling tower heat exchange system in which no individual
heat exchanger has greater than 100 ppmw HRVOCs in the process side fluid
is exempt from the requirements of this division, with the exception of the
recordkeeping requirements of §115.766(b) and (c) of this title.
(3)
Any account for which no stream directed to a cooling tower
heat exchange system contains 5.0% or greater by weight HRVOC is exempt from
the requirements of §115.761 of this title (relating to Site-wide Cap).
(4)
Any cooling tower heat exchange system that will be permanently
out of service by April 1, 2006 is exempt from the requirements of this division,
with the exception of the recordkeeping requirements in §115.766(j) of
this title.
§115.769.Counties and Compliance Schedules.
(a)
The owner or operator of each cooling tower
heat exchange system in Brazoria, Chambers, Fort Bend, Galveston, Harris,
Liberty, Montgomery, and Waller Counties shall demonstrate compliance with
this division (relating to Cooling Tower Heat Exchange Systems) as soon as
practicable, but no later than December 31, 2005, with the exception of
§115.761(a) - (c)
[
(b)
For cooling tower heat exchange systems
that become subject to the requirements of this division after December 31,
2005, testing and monitoring must be conducted as soon as practicable, but
no later than 60 days after being brought into highly-reactive volatile organic
compound service.
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 June 25, 2004.
TRD-200404257
Stephanie Bergeron
Director, Environmental Law Division
Texas Commission on Environmental Quality
Earliest possible date of adoption: August 8, 2004
For further information, please call: (512) 239-6087
30 TAC §§115.766 - 115.768
(Editor's note: The text of the following sections proposed for
repeal will not be published. The sections may be examined in the offices
of the Texas Commission on Environmental Quality or in the Texas Register
office, Room 245, James Earl Rudder Building, 1019 Brazos Street, Austin.)
STATUTORY AUTHORITY
The repeals are proposed under Texas Water Code, §5.103, concerning
Rules, and §5.105, concerning General Policy, that authorize the commission
to adopt rules necessary to carry out its powers and duties under the Texas
Water Code; and under Texas Health and Safety Code, §382.017, concerning
Rules, that authorizes the commission to adopt rules consistent with the policy
and purposes of the Texas Clean Air Act. The repeals are also proposed under
Texas Health and Safety Code, §382.002, concerning Policy and Purpose,
that establishes the commission's purpose to safeguard the state's air resources,
consistent with the protection of public health, general welfare, and physical
property; §382.011, concerning General Powers and Duties, that authorizes
the commission to control the quality of the state's air; §382.012, concerning
State Air Control Plan, that authorizes the commission to prepare and develop
a general, comprehensive plan for the proper control of the state's air; and §382.016,
concerning Monitoring Requirements Examination of Records, that authorizes
the commission to prescribe reasonable requirements for measuring and monitoring
the emissions of air contaminants.
The proposed repeals implement Texas Health and Safety Code, §§382.002,
382.011, 382.012, and 382.017.
§115.766.Testing Requirements.
§115.767.Recordkeeping Requirements.
§115.768.Exemptions.
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 June 25, 2004.
TRD-200404258
Stephanie Bergeron
Director, Environmental Law Division
Texas Commission on Environmental Quality
Earliest possible date of adoption: August 8, 2004
For further information, please call: (512) 239-6087
30 TAC §§115.780 - 115.783, 115.786 - 115.789
STATUTORY AUTHORITY
The amendments are proposed under Texas Water Code, §5.103, concerning
Rules, and §5.105, concerning General Policy, that authorize the commission
to adopt rules necessary to carry out its powers and duties under the Texas
Water Code; and under Texas Health and Safety Code, §382.017, concerning
Rules, that authorizes the commission to adopt rules consistent with the policy
and purposes of the Texas Clean Air Act. The amendments are also proposed
under Texas Health and Safety Code, §382.002, concerning Policy and Purpose,
that establishes the commission's purpose to safeguard the state's air resources,
consistent with the protection of public health, general welfare, and physical
property; §382.011, concerning General Powers and Duties, that authorizes
the commission to control the quality of the state's air; §382.012, concerning
State Air Control Plan, that authorizes the commission to prepare and develop
a general, comprehensive plan for the proper control of the state's air; and §382.016,
concerning Monitoring Requirements Examination of Records, that authorizes
the commission to prescribe reasonable requirements for measuring and monitoring
the emissions of air contaminants.
The proposed amendments implement Texas Health and Safety Code, §§382.002,
382.011, 382.012, and 382.017.
§115.780.Applicability.
(a)
Any process unit or process within a petroleum
refinery; synthetic organic chemical, polymer, resin, or methyl tert-butyl
ether manufacturing process; or natural gas/gasoline processing operation
in the Houston/Galveston area, as defined in §115.10 of this title (relating
to Definitions), in which a highly-reactive volatile organic compound [
(b)
An owner or operator may not use emission
reduction credits or discrete emission reduction credits in order to demonstrate
compliance with this division.
§115.781.General Monitoring and Inspection Requirements.
(a)
The owner or operator shall identify the components of
each process unit in highly-reactive volatile organic compound (HRVOC) service
that
[
(1) - (6)
(No change.)
(b)
Each component in the process unit must be monitored according
to the requirements of Subchapter D, Division 3 of this chapter (relating
to Fugitive Emission Control in Petroleum Refining, Natural Gas/Gasoline Processing,
and Petrochemical Processes in Ozone Nonattainment Areas), except that the
following additional requirements apply.
(1)
The exemptions of
§115.357(1) - (11)
[
(2)
(No change.)
(3)
The emissions from blind flanges, caps, or plugs at the
end of a pipe or line containing HRVOC; connectors; heat exchanger heads;
sight glasses; meters; gauges; sampling connections; bolted manways; hatches;
agitators; sump covers; junction box vents; covers and seals on volatile organic
compound [
(4)
(No change.)
(5)
All process drains equipped with water seal controls, as
defined in §115.140 of this title (relating to Industrial Wastewater
Definitions), shall be inspected weekly to ensure that the water seal controls
are effective in preventing ventilation, except that daily inspections are
required for those seals that have failed three or more inspections in any
12-month period. Upon request by the executive director,
United States
Environmental Protection Agency
[
(6)
All process drains not equipped with water seal controls
shall be inspected monthly to ensure that all gaskets, caps, and/or plugs
are in place and that there are no gaps, cracks, or other holes in the gaskets,
caps, and/or plugs. In addition, all caps and plugs shall be inspected monthly
to ensure that they are
tightly fitting
[
(7)
An unsafe-to-monitor or difficult-to-monitor component
for which quarterly monitoring is specified may instead be monitored as follows.
(A)
An unsafe-to-monitor component is a component that the
owner or operator determines is unsafe to monitor because monitoring personnel
would be exposed to an immediate danger as a consequence of conducting quarterly
monitoring. Components
that
[
(B)
A difficult-to-monitor component is a component that cannot
be inspected without elevating the monitoring personnel more than two meters
above a permanent support surface
or that is below floors or deck gratings
requiring confined space entry as defined in 29 Code of Federal Regulations §1910.146
. A difficult-to-monitor component for which quarterly monitoring is
specified may instead be monitored annually.
(8)
All pressure relief valves in gaseous service [
(9) - (10)
(No change.)
(c) - (d)
(No change.)
(e)
Any pressure relief device
that
[
(f)
(No change.)
(g)
Except as provided in paragraph (2) of
this subsection, the owner or operator shall use dataloggers and/or electronic
data collection devices during all monitoring required by this section. The
owner or operator shall use best efforts to transfer, on a daily basis, electronic
data from electronic datalogging devices to the database required by §115.356
of this title (relating to Monitoring and Recordkeeping Requirements).
(1)
For all monitoring events in which an electronic data collection
device is used, the collected monitoring data must include the identification
of each component and each calibration run, the maximum screening concentration
detected, the time of monitoring (i.e., the time that the organic vapor concentration
is read or recorded for each component), a date stamp, an operator identification,
an instrument identification, and calibration gas concentrations and certification
dates. The acceptable rate for recording data must be determined individually
by each owner or operator considering such factors including, but not limited
to, the size of the equipment, the equipment type, the accessibility of the
equipment, the number of leakers being found, and the skill of the monitoring
technicians. Each owner or operator shall have a documented auditing process
in place to assure proper calibration, identify response time failures, and
assess pace anomalies.
(2)
The owner or operator may use paper logs where necessary
or more feasible (e.g., small rounds (less than 100 components), re-monitoring
following component repair, or when dataloggers are broken or not available),
and shall record, at a minimum, the information required in paragraph (1)
of this subsection. For audio, visual, and olfactory inspections, the owner
or operator shall record, at a minimum, the identification of the person conducting
the inspection, the date, and the area that was inspected. The owner or operator
shall transfer any manually recorded monitoring data to the database required
by §115.356 of this title within seven days of monitoring.
(3)
Each change to the database regarding the monitored concentration,
date and time read, repair information, addition or deletion of components,
or monitoring schedule must be detailed in a log or inserted as a notation
in the database. All such changes must include the name of the person who
made the change, the date of the change, and an explanation to support the
change.
§115.782.Procedures and Schedule for Leak Repair and Follow-up.
(a) - (b)
(No change.)
(c)
Delay of repair.
(1)
For all components (except valves [
(A)
(No change.)
(B)
if the repair of a component within seven or 15 days (as
specified in subsection (b) of this section) after the leak is detected would
require a process unit shutdown
that
[
(i)
the owner or operator maintains, and makes available
upon request, documentation to authorized representatives of the United States
Environmental Protection Agency (EPA), the executive director, and any local
air pollution control agency having jurisdiction which includes a calculation
of:
[
(I)
the expected mass emissions resulting
from the next scheduled process unit shutdown, clearing, and subsequent startup
of the unit, including the basis for the calculation and all assumptions made;
(II)
the mass emission rates from each leaking
component in the process unit for which delay of repair is sought as determined
by using the methods in the EPA correlation approach in Section 2.3.3 of the
EPA guidance document "Protocol for Equipment Leak Emission Estimates," (EPA-453/R-95-017,
November, 1995) alone or in combination with the mass emission sampling approach
in Chapter 4 of the guidance document (EPA-453/R-95-017, November, 1995).
To use the EPA correlation approach, the estimated hourly mass emission rate
for each component shall be based on the average of the component's current
screening concentration and the previous screening concentration using Test
Method 21 for the days between the two monitoring efforts, and the last screening
concentration shall be used for the days following that last monitoring through
the date of the planned process unit shutdown. Where the monitoring instrument
is not calibrated to read past the leak definition or 100,000 ppmv, the pegged
emission rate values in Tables 2-13 and 2-14 in Section 2.3.3 of the EPA guidance
document "Protocol for Equipment Leak Emission Estimates" shall be used as
appropriate. Leaking components in heavy liquid service shall be assigned
the appropriate screening range leak rate for greater than 10,000 ppmv as
defined in Section 2.3.2 of the guidance document. As an alternative, the
heavy liquid component may be monitored using Test Method 21, and the actual
screening concentration may be used to calculate the mass emission rate using
the correlations in Section 2.3.3 of the guidance document. If the mass emission
sampling approach is used, it replaces the estimated emissions rate of the
EPA correlation approach in the calculation;
(III)
the cumulative mass emissions from each
leaking component in HRVOC service in the process unit for which delay of
repair is sought, from the date the leak is found through the date of the
next planned process unit shutdown; and
(IV)
the total cumulative mass emissions in
the process unit from the calculations made in subclause (III) of this clause
for leaking components in HRVOC service in the unit for which delay of repair
is sought; and
(ii)
the total cumulative mass emissions from
leaking components in HRVOC service in the process unit for which delay of
repair is sought as determined in clause (i)(IV) of this subparagraph, assessed
from the time that each additional leaking component is identified or at the
time of any other changes to the emissions estimates, from the date of the
change forward, will be less than the mass emissions resulting from shutdown,
clearing, and subsequent startup of the unit as determined in clause (i)(I)
of this subparagraph; or
(iii)
as an alternative to the requirements
of clause (i) and (ii) of this subparagraph, delay of repair is allowed for
each leaking component for which the owner or operator has chosen to undertake
"extraordinary efforts" to repair the leak. For purposes of this subparagraph,
"extraordinary efforts" is defined as nonroutine repair methods (e.g., sealant
injection) or utilization of a closed-vent system to capture and control the
leaks by at least 90%. For leaks detected over 10,000 ppmv, extraordinary
efforts shall be undertaken within 22 calendar days after the leak is found;
however, the owner or operator may keep the leaking valve on the shutdown
list only after two unsuccessful attempts to repair a leaking valve through
extraordinary efforts, provided that the second extraordinary effort attempt
is made within 37 calendar days after the leak is found. For all other leaks,
extraordinary efforts shall be undertaken within 30 calendar days after the
leak is found, and a second extraordinary effort attempt is not required.
(iv)
[
(C)
(No change.)
(2)
For valves
that
[
(A)
repair or replacement of these valves occurs at the next
scheduled process unit shutdown; and
(i)
the owner or operator has undertaken "extraordinary efforts"
to repair the leaking valve. For purposes of this subparagraph, "extraordinary
efforts" is defined as nonroutine repair methods (e.g., sealant injection)
or utilization of a closed-vent system to capture and control the leaks by
at least 90%. For leaks detected over 10,000 ppmv, extraordinary efforts shall
be undertaken within
14 calendar days after the leak is found
[
(ii)
the owner or operator maintains, and makes available upon
request, documentation to authorized representatives of EPA, the executive
director, and any local air pollution control agency having jurisdiction
that
[
(B)
(No change.)
§115.783.Equipment Standards.
The following equipment standards [
(1)
(No change.)
(2)
Whenever highly-reactive volatile organic compound [
[(A)
Recovery devices (e.g., condensers and
absorbers) used to comply with this paragraph must be designed and operated
to recover the HRVOC emissions vented to them with an efficiency of 95% or
greater.]
[(B)
Flares used to comply with this paragraph
must meet the requirements of:]
[(i)
Division 1 of this subchapter (relating to Vent Gas Control);
and]
[(ii)
40 Code of Federal Regulations §60.18 (b) or §63.11(b).]
[(C)
All other control devices used to comply
with this paragraph must reduce HRVOC emissions with a control efficiency
of at least 98% or to an HRVOC concentration of no more than 20 parts per
million by volume (on a dry basis corrected to 3.0% oxygen for combustion
devices).]
[(3)
Each pressure relief valve in gaseous
HRVOC service that vents to atmosphere which is installed in series with a
rupture disk, pin, second relief valve, or other similar leak-tight pressure
relief component, shall be equipped with a pressure sensing device or an equivalent
device or system between the pressure relief valve and the other pressure
relief component to monitor for leakage past the first component. When leakage
is detected past the first component, that component shall be repaired or
replaced as soon as practicable, but no later than 30 calendar days after
the failure is detected. As an alternative, the owner or operator may repair
or replace that component at the next planned process unit shutdown, but the
emissions are considered to be vent gas emissions and are subject to the site-wide
cap in §115.722 of this title (relating to Site-wide Cap and Control
Requirements).]
(3)
[
(A)
Acceptable shaft sealing systems include:
(i)
seals equipped with piping capable of transporting any
leakage from the seal(s) back to the process;
(ii)
seals with a closed-vent system capable of transporting
to a control device any leakage from the seal or seals;
(iii)
dual seals with a heavy liquid or
non-volatile organic
compounds
[
(iv)
seals with an automatic seal failure detection and alarm
system.
(B)
The executive director may approve shaft sealing systems
different from those specified in subparagraph (A) of this paragraph. The
executive director:
(i)
shall consider on a case-by-case basis the technological
circumstances of the individual pump, compressor, or agitator; and
(ii)
must determine that the alternative shaft sealing system
will result in the lowest emissions level that the pump, compressor, or agitator
is capable of meeting after the application of best available control technology
before approving the alternative shaft sealing system.
(C)
Any owner or operator affected by the executive director's
decision to deny a request for approval of an alternative shaft sealing system
may file a motion to overturn the executive director's decision. The requirements
of §50.139 of this title (relating to Motion to Overturn Executive Director's
Decision) apply. Executive director approval does not necessarily constitute
satisfaction of all federal requirements nor eliminate the need for approval
by
the United States Environmental Protection Agency
[
(4)
[
(A)
If water seal controls, as defined in §115.140
of this title
(relating to Industrial Wastewater Definitions), are used:
(i)
the only acceptable alternative to water as the sealing
liquid in a water seal is the use of ethylene glycol, propylene glycol, or
other low vapor pressure antifreeze,
that
[
(ii)
as an alternative to the weekly water seal inspections
of §115.781(b)(5) of this title (relating to General Monitoring and Inspection
Requirements), the owner or operator may choose to equip the process drain
with:
(I)
an alarm that alerts the operator if the water level in
the vertical leg of the drain falls below 50% of the maximum level, and a
device that continuously records the status of the water level alarm, including
the time period for which the alarm has been activated; or
(II)
a flow-monitoring device indicating either positive flow
from a main to a branch water line supplying a trap or water being continuously
dripped into the trap; and a device that continuously records the status of
water flow into the trap.
(B)
For process drains not equipped with water seal controls,
the process drain shall be equipped with:
(i)
a gasketed seal; or
(ii)
a tightly-fitting cap or plug.
(5)
[
§115.786.Recordkeeping Requirements.
(a)
(No change.)
(b)
If securing the bypass line valve in the closed position
to comply with §115.783(1)(B) of this title, the owner or operator shall:
(1) - (2)
(No change.)
(3)
maintain a record of each time the bypass line valve was
opened, including:
(A) - (C)
(No change.)
(D)
the
estimated
flow
rate
through the
valve; and
(E)
the resulting [
(c)
Records of all non-repairable components subject to
§115.782(c)
[
(1) - (5)
(No change.)
(d)
The owner or operator shall maintain records in accordance
with §115.356 of this title (relating to Monitoring and Recordkeeping
Requirements), including records identifying
, by one or more of the methods
specified in §115.781(a)(1) - (6) of this title (relating to General
Monitoring and Inspection Requirements),
and justifying each exemption
claimed exempt under §115.787 of this title (relating to Exemptions).
Except that the following additional requirements also apply:
(1)
the calculation showing the estimated
volatile organic compound (VOC) emission rates of the component as required
by §115.782(c)(1)(B)(i)(II) of this title if extraordinary efforts are
not going to be initiated; and
(2)
records for each process unit with leaking
components, updated each day after a leaking component is determined to require
a process unit shutdown to repair and where extraordinary efforts to repair
the component will not be pursued, including the following:
(A)
the date, calculations, and estimated VOC emissions as
required by §115.782(c)(1)(B)(i)(III) of this title;
(B)
the date, calculations, and comparison of VOC emissions
as required by §115.782(c)(1)(B)(i)(IV) of this title; and
(C)
the date of each process unit shutdown required due to
VOC emissions of leaking components exceeding the expected VOC emissions from
the shutdown.
(e)
The owner or operator shall maintain a
record of the results of all monitoring and inspections conducted in accordance
with §115.781 of this title.
(f)
[
§115.787.Exemptions.
(a)
Components that contact a process fluid
containing
[
(b)
The following are exempt from the shaft sealing system
requirements of
§115.783(2)
[
(1) - (2)
(No change.)
(c)
The following components are exempt from the requirements
of this division:
(1)
conservation vents or other devices on atmospheric storage
tanks that are actuated either by a vacuum or a pressure of no more than 2.5
pounds per square inch[
(2) - (3)
(No change.)
(4)
any account
[
(5)
components
that
[
(6)
sampling connection systems, as defined in 40 Code of Federal
Regulations (CFR) §63.161 (January 17, 1997),
that meet the requirements
of
[
(7)
instrumentation systems, as defined in 40 CFR §63.161
(January 17, 1997),
that meet the requirements of
[
(d)
(No change.)
[(e)
Each pressure relief valve equipped with
a rupture disk is exempt from the requirements of §115.781(b)(8) of this
title, provided that the pressure relief valve complies with §115.783(3)
of this title.]
(e)
[
(1)
pressure relief valves;
(2)
open-ended valves or lines in an emergency shutdown system
that
[
(3)
open-ended valves or lines containing materials
that
[
(4)
valves rated greater than 10,000 psig.
(f)
Any process unit with less than 50 components
in highly-reactive volatile organic compound service is exempt from §115.788
of this title (relating to the Audit Provision).
§115.788.Audit Provisions.
(a)
At least once every [
(1)
verify that
all components
are properly
tagged in accordance with §115.782(a) of this title (relating to Procedures
and Schedule for Leak Repair and Follow-up);
[
[(A)
were not tagged, but which should have
been tagged; or]
[(B)
were not included in the list of components
to be monitored (with a hydrocarbon gas analyzer) or visually inspected, but
which should have been included on that list;]
(2)
perform a field survey to determine the representative
percentage of leaking components in the audited process unit
[
(A)
The field survey must
[
(B)
The
[
Figure: 30 TAC §115.788(a)(2)(B) (No change.)
(C)
The field survey of a specific process unit must
[
(D)
the independent third-party organization
shall perform the field survey in accordance with Test Method 21 (40 Code
of Federal Regulations Part 60, Appendix A).
(3)
conduct a review of
all data generated by monitoring
technicians in the previous quarter. This
review must
[
(A)
a review of the number of components monitored per technician
and the time between monitoring events to validate the sampling procedures
accurately reflect the requirements of Test Method 21 including identification
of specific instances that a monitoring technician recorded data faster than
was physically possible due to the hydrocarbon gas analyzer response time
and/or the time required for the technician to move to the next component
;
(B)
a review of records to verify that the calibration
requirements of Test Method 21 have been properly implemented
[
(C)
identification of [
[(D)
identification of any discrepancies between
the data in the electronic database required by §115.356(2) of this title
(relating to Monitoring and Recordkeeping Requirements) and the data in the
datalogger and/or field notes of §115.354(10)(A) and (B) of this title
(relating to Inspection Requirements), respectively.]
(b)
For purposes of this section,
an
independent
third-party organization
is
[
(c)
The owner or operator shall submit
a verbal
notification
to the
Houston
[
[(1)
verbal notification of the date that
the independent third-party organization is scheduled to begin the audit at
least 30 days prior to such date; and]
[(2)
written notification within 15 days after
the audit is completed.]
(d)
The owner or operator shall furnish the
Houston
[
(1)
the number of components
that
[
[(2)
the number of components which were not
included in the list of components to be monitored (with a hydrocarbon gas
analyzer) or visually inspected, but which] should have been included on that
list;]
(2)
[
(A)
valves (excluding pressure relief valves);
(B)
pressure relief valves;
(C)
pumps;
(D)
compressors; and
(E)
connectors; [
(3)
[
[(A)
the number of components monitored per
technician;]
[(B)
the time between monitoring events, including
identification of specific instances in which a monitoring technician recorded
data faster than was physically possible due to the hydrocarbon gas analyzer
response time and/or the time required for the technician to move to the next
component; and]
[(C)
identification of abnormal data patterns].
(e)
If the results of the independent third-party
audit indicate deficiencies in the implementation of Test Method 21, the owner
or operator shall submit a corrective action plan with the audit report to
the Houston regional office or any local air pollution control agency having
jurisdiction.
(f)
[
(g)
[
(1)
includes a detailed explanation of how the equivalency
will be demonstrated, including the appropriate recordkeeping and reporting
requirements that will be implemented
that
[
(2)
demonstrates that it is a replicable procedure and details
how the equivalency will be demonstrated.
(h)
Upon review of the audit results, the
executive director may specify additional corrective actions beyond any potential
corrective actions submitted in the documentation required under subsection
(e) of this section.
§115.789.Counties and Compliance Schedules.
The owner or operator of each petroleum refinery; synthetic organic
chemical, polymer, resin, or methyl tert-butyl ether manufacturing process;
or natural gas/gasoline processing operation in Brazoria, Chambers, Fort Bend,
Galveston, Harris, Liberty, Montgomery, and Waller Counties shall demonstrate
compliance with the requirements of this division (relating to Fugitive Emissions)
in accordance with the following schedule.
(1)
The initial monitoring of all components for which monitoring
is required under this division, but [
(A)
the schedule in §115.781(f) of this title (relating
to General Monitoring and Inspection Requirements)
applies
[
(B)
(No change.)
(2)
All equipment upgrades required by §115.783 of this
title (relating to Equipment Standards) must be made as soon as practicable,
but no later than March 31, 2004, except that flares used to comply with the
requirements of §115.783(2)(B) of this title
must
[
(3)
The initial independent third-party audit required by §115.788
of this title (relating to Audit Provisions) shall be completed and the results
of the audit submitted to the executive director [
[(4)
The testing required by §115.785
of this title (relating to Testing Requirements) shall be conducted as soon
as practicable, but no later than December 31, 2005.]
(4)
[
(5)
[
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 June 25, 2004.
TRD-200404259
Stephanie Bergeron
Director, Environmental Law Division
Texas Commission on Environmental Quality
Earliest possible date of adoption: August 8, 2004
For further information, please call: (512) 239-6087
30 TAC §115.785
(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 Commission on Environmental Quality or in the Texas Register office,
Room 245, James Earl Rudder Building, 1019 Brazos Street, Austin.)
STATUTORY AUTHORITY
The repeal is proposed under Texas Water Code, §5.103, concerning
Rules, and §5.105, concerning General Policy, that authorize the commission
to adopt rules necessary to carry out its powers and duties under the Texas
Water Code; and under Texas Health and Safety Code, §382.017, concerning
Rules, that authorizes the commission to adopt rules consistent with the policy
and purposes of the Texas Clean Air Act. The repeal is also proposed under
Texas Health and Safety Code, §382.002, concerning Policy and Purpose,
that establishes the commission's purpose to safeguard the state's air resources,
consistent with the protection of public health, general welfare, and physical
property; §382.011, concerning General Powers and Duties, that authorizes
the commission to control the quality of the state's air; §382.012, concerning
State Air Control Plan, that authorizes the commission to prepare and develop
a general, comprehensive plan for the proper control of the state's air; and §382.016,
concerning Monitoring Requirements Examination of Records, that authorizes
the commission to prescribe reasonable requirements for measuring and monitoring
the emissions of air contaminants.
The proposed repeal implements Texas Health and Safety Code, §§382.002,
382.011, 382.012, and 382.017.
§115.785.Testing Requirements.
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 June 25, 2004.
TRD-200404260
Stephanie Bergeron
Director, Environmental Law Division
Texas Commission on Environmental Quality
Earliest possible date of adoption: August 8, 2004
For further information, please call: (512) 239-6087
Subchapter D. PETROLEUM REFINING, NATURAL GAS PROCESSING, AND PETROCHEMICAL PROCESSES
Chapter 115.
CONTROL OF AIR POLLUTION FROM VOLATILE ORGANIC COMPOUNDS
the Texas Clean Air
Act
] 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 Texas Clean Air
Act, the following terms, when used in this chapter (relating to Control of
Air Pollution from Volatile Organic Compounds), [
shall
] have the
following meanings, unless the context clearly indicates otherwise. Additional
definitions for terms used in this chapter are found in §3.2 and §101.1
of this title (relating to Definitions).
(VOC)
] in the air, determined at least one meter upwind
of the component to be monitored. Test Method 21 (40 Code of Federal Regulations
Part
[
(CFR)
] 60, Appendix A) shall be used to determine the
background.
VOC
] collected by a capture system
that
[
which
] is expressed as a percentage derived from the
weight per unit time of
VOCs
[
VOC
] entering a capture
system and delivered to a control device divided by the weight per unit time
of total
VOCs
[
VOC
] generated by a source of
VOCs
[
VOC
].
VOC
].
(12)
] 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, an external
floating roof storage tank
that
[
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.
(13)
] Fugitive emission--Any
volatile organic compound
[
VOC
] entering the atmosphere
that
[
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)
] Heavy liquid--
Volatile
organic compounds that
[
VOCs which
] have a true vapor pressure
equal to or less than 0.044 pounds per square inch absolute [
(psia)
]
(0.3
kiloPascal
[
kPa
]) at 68 degrees Fahrenheit (20
degrees Celsius).
(17)
] Highly-reactive volatile
organic compound [
(HRVOC)
]--As follows.
VOCs
]: 1,3-butadiene; all isomers
of butene (e.g., isobutene (2-methylpropene or isobutylene), alpha-butylene
(ethylethylene)
,
and beta-butylene (dimethylethylene, including
both cis- and trans- isomers)); ethylene; and propylene.
(18)
] Houston/Galveston area--Brazoria,
Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties.
(19)
] Incinerator--For the purposes
of this chapter, an enclosed control device that combusts or oxidizes
volatile organic compound
[
VOC
] gases or vapors.
(20)
] Internal floating cover--A
cover or floating roof in a fixed roof tank
that
[
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, an external floating roof storage
tank
that
[
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.
(21)
] Leak-free marine vessel--A
marine vessel
with
[
whose
] cargo tank closures (hatch
covers, expansion domes, ullage openings, butterworth covers, and gauging
covers)
that
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
must
[
shall
] meet the applicable rules or regulations of
the marine vessel's classification society or flag state. Cargo tank pressure/vacuum
valves
must
[
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.
(22)
] Light liquid--
Volatile
organic compounds that
[
VOCs which
] have a true vapor pressure
greater than 0.044
pounds per square inch absolute
[
psia
]
(0.3
kiloPascal
[
kPa
]) at 68 degrees Fahrenheit (20
degrees Celsius), and are a liquid at operating conditions.
(23)
] 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.
(24)
] Low-density polyethylene--A
thermoplastic polymer or copolymer comprised of at least 50% ethylene by weight
and having a density of 0.940 grams per cubic centimeter [
(g/cm
] or less.
(25)
] 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.
(26)
] 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.
(27)
] Marine terminal--Any marine
facility or structure constructed to transfer oil, gasoline, or other volatile
organic liquid bulk cargo to or from a marine vessel. A marine terminal may
include one or more marine loading facilities.
(28)
] Metal-to-metal seal--A connection
formed by a swage ring
that
[
which
] exerts an elastic,
radial preload on narrow sealing lands, plastically deforming the pipe being
connected, and maintaining sealing pressure indefinitely.
(29)
] 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.
(30)
] 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.
(31)
] Polymer or resin manufacturing
process--A process that produces any of the following polymers or resins:
polyethylene, polypropylene, polystyrene, and styrenebutadiene latex.
(32)
] Pressure relief valve--A
safety device used to prevent operating pressures from exceeding the maximum
allowable working pressure of the process equipment. A pressure relief valve
is automatically actuated by the static pressure upstream of the valve, but
does not include:
(psig)
].
(33)
] Printing line--An operation
consisting of a series of one or more printing processes and including associated
drying areas.
(34)
] Process drain--Any opening
(including a covered or controlled opening)
that
[
which
]
is installed or used to receive or convey wastewater into the wastewater system.
(35)
] Process unit--The smallest
set of process equipment that can operate independently and includes all operations
necessary to achieve its process objective.
(36)
] Rupture disk--A diaphragm
held between flanges for the purpose of isolating a
volatile organic
compound
[
VOC
] from the atmosphere or from a downstream pressure
relief valve.
(37)
] Shutdown or turnaround--For
the purposes of this chapter, a work practice or operational procedure that
stops production from a process unit or part of a unit during which time it
is technically feasible to clear process material from a process unit or part
of a unit consistent with safety constraints, and repairs can be accomplished.
(38)
] Startup--For the purposes
of this chapter, the setting into operation of a piece of equipment or process
unit for the purpose of production or waste management.
(39)
] Strippable volatile organic
compound (VOC)--Any VOC in cooling tower heat exchange system water
that
[
which
] is emitted to the atmosphere when the water
passes through the cooling tower. [
An estimate of total and speciated
strippable VOC is acceptable when measured by:
]
(40)
] 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
(October 17, 2000).
(41)
] 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.
(42)
] 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
that
[
which
] is used 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.
(43)
] True partial pressure--The
absolute aggregate partial pressure [
(psia)
] of all
volatile
organic compounds
[
VOC
] in a gas stream.
(44)
] Vapor balance system--A system
that
[
which
] provides for containment of hydrocarbon vapors
by returning displaced vapors from the receiving vessel back to the originating
vessel.
(45)
] Vapor control system or vapor
recovery system--Any control system
that
[
which
] utilizes
vapor collection equipment to route
volatile organic compounds (VOC)
[
VOC
] to a control device that reduces VOC emissions.
(46)
] 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.
(47)
] 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."
Subchapter H. HIGHLY-REACTIVE VOLATILE ORGANIC COMPOUNDS
shall
] have the following meanings, unless the context clearly
indicates otherwise. Additional definitions for terms used in this division
are found in §§3.2, 101.1, and 115.10 of this title (relating to
Definitions).
(1)
] Supplementary fuel--Natural
gas or fuel gas added to the gas stream to increase the net heating value
to the minimum required value.
(2)
] Pilot gas--Gas that is used
to ignite or continually ignite flare gas.
Emissions of highly-reactive
volatile organic compounds (HRVOC) at each account subject to this division
(relating to Vent Gas Control) or Division 2 of this subchapter (relating
to Cooling Tower Heat Exchange Systems) are limited to a 24-hour rolling average
as specified in Table 6-2.1, Initial HRVOC Site-Cap Allocations: Harris County,
and Table 6-2.2, Initial HRVOC Site-Cap Allocations: Seven Surrounding Counties,
of the
Post-1999 Rate-of-Progress and Attainment
Demonstration Follow-up SIP for the Houston/Galveston Ozone Nonattainment
Area
adopted on December 13, 2002.
]
(b)
] All flares
must
[
shall
] continuously meet the requirements of 40 Code of Federal Regulations
§60.18(c)(2) - (6) and (d)
[
§60.18(c) - (f)
] as
amended through October 17, 2000 (65 FR 61744) when vent gas containing volatile
organic compounds is being routed to the flare.
(c)
] An owner or operator may not
use emission reduction credits or discrete emission reduction credits in order
to demonstrate compliance with this division.
Each
] vent
gas stream
that is not controlled by a flare
at an account must
be tested by applying the appropriate reference method tests and procedures
specified in §115.125 of this title (relating to Testing Requirements)
to establish maximum potential highly-reactive volatile organic compound (HRVOC)
hourly emission data expected during any operation not defined as an emissions
event or a scheduled maintenance, startup, or shutdown activity under §101.1
of this title (relating to Definitions). The data shall be used in accordance
with the test plan required under §115.726 of this title (relating to
Recordkeeping and Reporting Requirements) to demonstrate compliance with the
control requirement of
§115.722(a) - (c)
[
§115.722(a)
] of this title (relating to Site-wide Cap and Control Requirements).
For cyclic or batch processes, the HRVOC emissions shall be considered as
zero during non-operational periods other than startup, shutdown, or maintenance
activities.
Alternatives to
] the testing requirements of subsection
(a) of this section, for vent gas streams that are not controlled by a flare
or are not pressure relief valves. The vent gas stream shall comply with the
process parameter monitoring requirements of subsection (a) of this section:
[
, include the following.
]
annually
] thereafter be subjected to a cylinder gas audit
per 40 CFR Part 60, Appendix B, Performance Specification 2, Section 16 to
assess system bias and ensure accuracy; and
(C)
] steam system vents; [
or
]
(D)
] vent gas streams where there
is no HRVOC present except during emissions events
; or
[
.
]
subsection (e)
] of this section, the owner or operator of an affected
flare
must
[
shall
] conduct continuous monitoring,
to demonstrate compliance with §115.722(a) - (d) of this title
as
follows:
shall
] be capable of measuring the entire gas stream flow to the flare
(i.e., all vent gas and supplemental fuel sources) and may consist of one
or more flow measurements at one or more header locations. For correcting
flow rate to standard conditions (defined as 68 degrees Fahrenheit and 760
millimeters of mercury (mm Hg)), temperature and pressure in the main flare
header
must
[
shall
] be monitored continuously. The monitors
must
[
shall
] be calibrated to meet accuracy specifications
as follows:
shall
]
be calibrated annually to within ±2.0% at absolute temperature;
shall
]
be calibrated annually to within ±5.0 mm Hg; and
shall
] be initially calibrated, prior
to installation, to demonstrate accuracy to within 5.0% at flow rates equivalent
to 30%, 60%, and 90% of monitor full scale. After installation, the flow monitor
or velocity monitor
must
[
shall
] be calibrated annually
according to manufacturer's specifications;
shall
] also be capable of measuring,
at least once every 15 minutes, other potential constituents (e.g., hydrogen,
nitrogen, methane, and carbon dioxide, and volatile organic compounds (VOC)
other than HRVOCs) sufficient to determine the molecular weight and net heating
value of the gas combusted in the flare to within 5.0%. Samples
must
[
shall
] be collected from a location on the main flare header
such that the measured constituents, including any supplementary fuel, is
representative of the combined gas combusted in the flare system.
Net
heating value of the gas combusted in the flare must be calculated according
to the equation given in 40 CFR §60.18(f)(3) as amended through October
17, 2000 (65 FR 61744). The samples must be used to demonstrate continuous
compliance with the requirements of §115.722(a) - (d) of this title.
Pilot gas may not be included in the determination of the net heating value.
shall
] be performed
at least once every calendar quarter instead of once every month, and the
mid-level calibration check procedure in Section 10.2 of Performance Specification
9
must
[
shall
] be performed at least once every calendar
week instead of once every 24 hours. The calibration gases used for calibration
procedures
must
[
shall
] be in accordance with Section
7.1 of Performance Specification 9
;
[
. Net heating value of
the gas combusted in the flare shall be calculated according to the equation
given in 40 CFR §60.18(f)(3) as amended through October 17, 2000 (65
FR 61744). The samples shall be used to continuously meet the minimum net
heating value requirements of 40 CFR §60.18 and the site-wide cap of §115.722
of this title. Pilot gas shall not be included in the determination of the
net heating value;
]
;
]
24
]
hours of the initial on-line analyzer malfunction. The sampling location must
be such that the measured constituents, including any supplementary fuel,
is representative of all of the major constituents going to the flare system.
For determining the HRVOC concentrations in the flare header gas, the samples
must
[
shall
] be analyzed for the concentrations of HRVOC
according to the procedures in 40 CFR Part 60, Appendix A, Method 18 as amended
through October 17, 2000 (65 FR 61744). Samples
must
[
shall
] also be analyzed by American Standard of Testing Materials Standard
D1946-77 to determine other potential constituents (e.g., hydrogen, nitrogen,
methane, and carbon dioxide, and VOCs other than HRVOCs) sufficient to determine
the molecular weight and net heating value of the gas combusted in the flare
to within 5.0%. Net heating value of the gas combusted in the flare
must
[
shall
] be calculated according to the equation given
in 40 CFR §60.18(f)(3). During periods of monitor downtime, these samples
must
[
shall
] be used to demonstrate
continuous compliance
with the requirements of §115.722(a) - (d) of this title
[
that the minimum net heating value requirements of 40 CFR §60.18 and
the site-wide cap of §115.722 of this title
] are met;
shall
] not be included in the determination
of the net heating value. [
Average net heating value over an one-hour
block period will be used to demonstrate compliance with the minimum net heating
value requirements of §115.722(b) of this title;
]
(6)
] calculate the HRVOC hourly
average mass emission rates from the flare using the data gathered according
to paragraphs
(1) - (6)
[
(1) - (4)
] of this subsection,
assuming a 99% destruction efficiency for ethylene and propylene and a 98%
destruction efficiency for all other HRVOCs when the flare meets the heating
value and exit velocity requirements of 40 CFR 60.18. During each 15-minute
period when the flare is not in compliance with the
net
heating
value or exit velocity requirements of 40 CFR §60.18, a destruction efficiency
of 93% shall be assumed to calculate HRVOC mass emission rates
.
[
;
]
or temporary portable flares used solely for the abatement of emissions
from scheduled maintenance or startup or shutdown activities
] are not
required to comply with the monitoring requirements of subsection (d) of this
section, provided the following specific requirements are satisfied.
(A)
]
To demonstrate compliance
with the minimum net heating value requirements of §115.722(d) of this
title, a
[
A
] calorimeter
must
[
shall
]
be calibrated, installed, operated, and maintained, in accordance with manufacturer
recommendations, to continuously measure and record the net heating value
of the gas sent to the flare, in British thermal units/standard cubic foot
of the gas.
(C)
] The flare's actual exit velocity
for each loading activity
must
[
shall
] be calculated
every 15 minutes, based on the maximum loading rate and the supplemental fuel
rate corrected to standard temperature and pressure and the unobstructed (free)
cross-sectional area of the flare tip, according to 40 CFR §60.18(f)(4)
to demonstrate compliance with the exit velocity requirements of §115.722(d)
of this title
.
(D)
] The HRVOC hourly average mass
emission rates from the flare
must
[
shall
] be calculated
to demonstrate compliance with the site-wide cap in §115.722 of this
title
, using total HRVOC sent to the flare calculated based on loading
emission calculations [
approved by the commission
], and the speciated
composition of the material being sent to the flare, assuming a 99% destruction
efficiency for ethylene and propylene and a 98% destruction efficiency for
all other HRVOCs when the flare meets the
net
heating value and
exit velocity requirements of 40 CFR
§60.18
[
60.18
].
During each 15-minute period when the flare does not meet the
net
heating
value or exit velocity requirements of 40 CFR §60.18, a destruction efficiency
of 93%
must
[
shall
] be assumed to calculate HRVOC mass
emission rates.
(f)
]
Minor modifications
[
Modifications
] to
either
test methods or
monitoring
[
alternative test
] methods may be approved by the executive
director. Test methods other than those specified in [
subsections (a)
- (c) and (e) of
] this section may be used if approved by the executive
director and validated by 40 CFR Part 63, Appendix A, Test Method 301 (December
29, 1992). For the purposes of this subsection, substitute "executive director"
in each place that Test Method 301 references "administrator."
review and
] approval a test plan for testing and a quality
assurance plan (QAP) for the monitoring requirements (including installation,
calibration, operation, and maintenance of continuous emissions monitoring
systems) of this division (relating to Vent Gas Control)
and subsequently
comply with the conditions outlined in the approved test plan or QAP
as
follows:
at least 60 days prior to being
placed in highly-reactive volatile organic compound (HRVOC) service
];
and
and
]
.
]
maintain a record of the results of all testing conducted in accordance with §115.725
of this title.
]
(c)
] The owner or operator of a
flare at an account that is subject to §115.722 of this title (relating
to Site-wide Cap and Control Requirements) or the continuous monitoring requirements
of
§115.725
[
§115.725(d) or (e)
] of this title
shall comply with the following recordkeeping requirements:
,
] taken by documenting the
dates, reasons, and durations of such occurrences; [
and
]
.
]
(d)
] Records for exemptions
in §115.727(a) - (e) of this title (relating to Exemptions)
shall
include the following.
(relating to Exemptions)
]
shall maintain records to document that each vent gas stream
that is
routed to a flare contains less than 5.0% by weight HRVOC at all times
and
each vent
gas stream not
routed to a flare does not exceed 100
parts per million by volume HRVOC at any time.
which
] document
that the HRVOC content of the gas stream that is routed to the flare does
not exceed 5.0% by weight at any time.
which
] demonstrate continuous compliance with the exemption criteria
of
§115.727(c)
[
§115.727(e)
] of this title;
or
which
] demonstrate continuous compliance with the exemption criteria of
§115.727(d)
[
§115.727(f)
] of this title.
(e)
] The owner or operator of each
account subject to §115.722 of this title shall maintain
daily
records
to demonstrate compliance with the tons per calendar year emissions limits
specified in §115.722(a) and (b) of this title, including
[
that update hourly the 24-hour rolling average HRVOC emissions which include
]:
which
] are subject to Division 2 of this subchapter (relating to Cooling
Tower Heat Exchange Systems);
and
continuously monitored vent gas and flare emissions; and
]
(f)
] The owner or operator shall
maintain
on-site,
all records required in this division and other
records as necessary to demonstrate continuous compliance and records of periodic
measurements for at least five years and make them available for review upon
request by authorized representatives of the executive director,
United
States Environmental Protection Agency
[
EPA
], or any local
air pollution control agency with jurisdiction.
(HRVOC)
] at all times and all individual
vent gas streams not routed to a flare contain less than 100 parts per million
by volume (ppmv)
HRVOCs
[
HRVOC
] at all times is exempt
from the requirements of §115.722(a) of this title (relating to Site-wide
Cap and Control Requirements).
HRVOC
]:
the site-wide cap of §115.722(a)
] of this title;
and
§115.725(d) and (e)
] of this
title (relating to
Recordkeeping and Reporting
[
Monitoring
and Testing
] Requirements) and
§115.726(d)
[
§115.726(c)
] of this title and is therefore not required to submit a quality assurance
plan under §115.726(a) of this title.
(e)
]
For
[
The following
] vent gas
streams that are not routed to a flare, the following
[
stream
] exemptions
may
apply
:
[
.
]
HRVOC
] is exempt from the requirements of this division,
with the exception of the recordkeeping requirements of
§115.726(e)(3)(A)
[
§115.726(d)(3)
] of this title.
HRVOC
], but that has an HRVOC concentration less
than 100 ppmv at all times
or has a maximum potential flow rate equal
to or less than 100 dry standard cubic feet per hour
[
, excluding
emissions events,
] is exempt from this division with the exception of
the recordkeeping requirements of
§115.726(e)(3)(A)
[
§115.726(d)(3)
] of this title
. The
[
, provided that
the
] maximum potential HRVOC emissions for the sum of all vent gas streams
claimed under this exemption, in pounds per hour,
must be
[
is
] less than 5.0% of the HRVOC cap for the account specified in §115.722(a)
or (b)
of this title.
§115.726(d)(3)
] of this title:
which
] maintain
working pressure sufficient at all times to prevent any vapor or gas loss
to the atmosphere;
(f)
] Any flare that at no time receives
a total gas stream with greater than 100 ppmv HRVOC is exempt from the requirements
of this division, with the exception of the recordkeeping requirements of
§115.726(c)(3)(B)
[
§115.726(d)(3)
] of this title.
shall
] be completed and the results submitted to the
Houston
[
appropriate
] regional office and any local air pollution
control agency with jurisdiction as soon as practicable, but no later than
December 31, 2005
for existing vent gas streams and pressure relief valves.
For vent gas streams and pressure relief valves that become subject to the
requirements of this division after December 31, 2005, testing and monitoring
must be conducted as soon as practicable, but no later than 60 days after
being brought into highly-reactive volatile organic compound service
.
the site-wide cap in §115.722
] of this title
(relating to Site-wide Cap and Control Requirements) for which the owner or
operator shall demonstrate compliance as soon as practicable, but no later
than April 1, 2006.
For flares that become subject to the requirements
of this division after December 31, 2005, testing and monitoring must be conducted
as soon as practicable, but no later than 60 days after being brought into
highly-reactive volatile organic compound service.
2.
COOLING TOWER HEAT EXCHANGE SYSTEMS
which
] emits or has
the potential to emit a highly-reactive volatile organic compound, as defined
in §115.10 of this title, is subject to the requirements of this division
(relating to Cooling Tower Heat Exchange Systems) in addition to the applicable
requirements of any other division in this subchapter or any other subchapter
in this chapter.
shall
] have the following meaning, unless the context clearly
indicates otherwise. Additional definitions for terms used in this division
are found in §§3.2, 101.1, and 115.10 of this title (relating to
Definitions). Cooling tower heat exchange system--Cooling towers, associated
heat exchangers, pumps, and ancillary equipment where water is used as a cooling
medium and the heat from process fluids is transferred to cooling water. This
does not include fin-fan coolers. This also does not include comfort cooling
tower heat exchange systems (i.e., those [
which are
] used exclusively
in cooling, heating, ventilation, and air conditioning systems).
Emissions of highly-reactive
volatile organic compounds at each account subject to this division (relating
to Cooling Tower Heat Exchange Systems) and Division 1 of this subchapter
(relating to Vent Gas Control) are limited to a 24-hour rolling average as
specified in Table 6-2.1, Initial HRVOC Site-Cap Allocations: Harris County,
and Table 6-2.2, Initial HRVOC Site-Cap Allocations: Seven Surrounding Counties,
of the
Post-1999 Rate-of-Progress and Attainment
Demonstration Follow-up SIP for the Houston/Galveston Ozone Nonattainment
Area
adopted on December 13, 2002.
]
(b)
] An owner or operator may not
use emission reduction credits or
discrete emission reduction credits
[
DERC
] in order to demonstrate compliance with this division.
greater than 100 parts per million by weight (ppmw) of highly-reactive
volatile organic compounds (HRVOC) in the process side fluid and
] a
design capacity to circulate 8,000 gallons per minute (gpm) or greater of
cooling water shall:
shall
] be collected for total VOC analysis according
to the
air-stripping method in Appendix P of the Texas Commission on
Environmental Quality Sampling Procedures Manual (January 2003)
[
Texas Commission on Environmental Quality (commission) air-stripping method
(Appendix P, Sampling Procedures Manual, January 2003)
]. This sample
must
[
shall
] be collected at least three times per calendar
week, with an interval of no less than 36 hours between samples;
HRVOC
] concentration by
collecting samples from each inlet of each cooling tower at least once per
month in accordance with
the air-stripping method in Appendix P
[
appropriate methods in §115.766 of this title (relating to Testing Requirements)
];
§115.766 of this title
] from each
inlet of the affected cooling tower at least once daily. The additional sampling
to determine speciated and total HRVOC shall continue on a daily basis until
the concentration of total strippable VOC drops below 50 ppbw; and
VOC
]
in paragraphs (4) and (5) of this subsection, a continuous on-line monitor
capable of providing total HRVOC and speciated HRVOCs in ppbw may be installed.
The continuous on-line monitor system must satisfy the requirements of
Sections 8.3, 10, 13.1, and 13.2
[
Subsections 8.2 and 8.3, Section
10, and Subsections 13.1 and 13.2
] of 40 Code of Federal Regulations
(CFR) Part 60, Appendix B, Performance Specification 9, as amended through
October 17, 2000 (65 FR 61744).
The multi-point calibration procedure
in Section 10.1 of Performance Specification 9 must be performed at least
once every calendar quarter instead of once every month.
During out-of-order
periods of the on-line HRVOC monitor(s),
sampling must be performed
[
a sample shall be collected
] for total and speciated HRVOC analysis
according to the air-stripping method in [
the commission's Sampling Procedures
Manual,
] Appendix P.
Sampling must
[
This sample shall
] be
performed
[
collected
] at least three times
per calendar week, with an interval of no less than 36 hours between
sampling times, until the continuous on-line monitor is properly operating
and within the required performance specifications
[
samples
].
greater than 100 ppmw of HRVOC in the process side fluid
and
] a design capacity to circulate less than 8,000 gpm of cooling water
shall:
shall
] be calibrated on an annual basis to within ±5.0% accuracy.
When the cooling tower flow monitor is down, flow measurements
must
[
shall
] be used for the most recent 24-hour period in which the flow
measurements are representative of cooling tower operations during monitor
downtime;
appropriate methods
in §115.766 of this title,
] with an interval of not less than 48
hours between samples;
shall be
operated
] as required by this section at least 95% of the time when
the cooling tower is operational, averaged over a calendar year
. The
percent measurement data availability must be calculated as the total operating
hours of the cooling tower heat exchange system for which valid quality-assured
data was recorded divided by the total operating hours of the cooling tower
heat exchange system. Time required for normal calibration checks required
under this subsection is not considered downtime for purposes of this calculation
;
appropriate methods in §115.766 of this title
];
calculated
]
total strippable VOC [
concentration
] is equal to or greater than
50 ppbw in the cooling tower water, collect
an
additional
sample
[
samples
] to determine total strippable VOC, speciated
HRVOC, and total HRVOC[
, in accordance with §115.766 of this title
] from each inlet of the affected cooling tower at least once daily
in accordance with the air-stripping method in Appendix P
. The additional
sampling to determine total strippable VOC, speciated [
HRVOC,
]
and total HRVOC
must
[
shall
] continue
on a daily
basis
until the concentration of total strippable VOC drops below 50
ppbw; and
VOC
]
in paragraphs (4) and (5) of this subsection, a continuous on-line monitor
capable of providing total HRVOC and speciated HRVOCs in ppbw may be installed.
The continuous on-line monitor system must satisfy the requirements of
Sections 8.3, 10, 13.1, and 13.2
[
Subsections 8.2 and 8.3, Section
10, and Subsections 13.1 and 13.2
] of 40 CFR Part 60, Appendix B, Performance
Specification 9.
The multi-point calibration procedure in Section 10.1
of Performance Specification 9 must be performed at least once every calendar
quarter instead of once every month.
During out-of-order periods of
the on-line HRVOC monitor(s),
sampling must be performed
[
a sample shall be collected
] for total and speciated HRVOC analysis
according to the air-stripping method in [
the commission's Sampling Procedures
Manual,
] Appendix P.
Sampling must
[
This sample shall
] be
performed
[
collected
] at least twice per
calendar week, with an interval of no less than 72 hours between
sampling
times, until the continuous on-line monitor is properly operating and within
the required performance specifications
[
samples
].
The
] owner or operator of the cooling tower heat exchange system shall
determine the speciated HRVOC concentration as soon as this information is
available, but no later than seven days after the sample(s) have been collected.
Samples collected in a Tedlar
TM
bag must be analyzed
no later than 72 hours after the samples have been collected.
The samples
must be analyzed according to the procedures in Test Method 18, 40 CFR Part
60, Appendix A, and/or Method TO-14A, published in "U.S. EPA Compendium for
Determination of Toxic Organic Compounds in Ambient Air (1996)," United States
Environmental Protection Agency Document Number 625/R96/010B.
(e)
] In lieu of subsections (a)(2)
- (5) and (b)(2) - (5) of this section, the owner or operator of cooling tower
heat exchange systems in which no individual heat exchanger has 5.0% or greater
HRVOC in the process-side fluid, shall determine total strippable VOC and
the HRVOC concentration in the cooling tower water at least once per month,
with an interval of not less than 20 days between samples,
according
to the air-stripping method in Appendix P
[
in accordance with appropriate
methods in §115.766 of this title
]. If the total strippable VOC
concentration in the cooling tower water is 50 ppbw or greater, the owner
or operator shall determine the total strippable VOC weekly and the HRVOC
concentration weekly. The additional sampling for the total strippable VOC
concentration and HRVOC concentration [
shall
] continue until the
total strippable VOC concentration drops below 50 ppbw.
(f)
] In lieu of using a continuous
flow monitor as described in subsections (a)(1) and (b)(1) of this section,
the owner or operator of
a
cooling tower heat exchange
system
[
systems
] may:
subsection (d) of this section
], a calculation methodology
that
[
which
] will provide, on a continuous basis, the cooling
water circulation flow rate (in gpm) based on the following: cooling water
discharge pressure for each pump; the manufacturer's certified pump performance
data; and the number of pumps in operation. This calculated flow rate will
then be used to determine the hourly emission rate in pounds per hour, as
required by
§115.766(a)(3)
[
§115.767(a)(3)
]
of this title [
(relating to Recordkeeping Requirements)
].
(g)
] Minor modifications to
the
[
these
] monitoring
and testing
methods
in this section
may be approved by the executive director. Monitoring
and testing
methods other than those specified in subsections
(a) - (e)
[
(a), (b), (e), and (f)
] of this section may be
used if approved by the executive director and validated by 40 CFR Part 63,
Appendix A, Test Method 301 (December 29, 1992). For the purposes of this
subsection, substitute "executive director" in each place that Test Method
301 references "administrator."
the site-wide cap in §115.761
]
of this title (relating to Site-wide Cap) for which the owner or operator
shall demonstrate compliance as soon as practicable, but no later than April
1, 2006.
3.
FUGITIVE EMISSIONS
(VOC)
], as defined in §115.10 of this title, is a raw material,
intermediate, final product, or in a waste stream is subject to the requirements
of this division (relating to Fugitive Emissions) in addition to the applicable
requirements of Subchapter D, Division 3 of this chapter (relating to Fugitive
Emission Control in Petroleum Refining, Natural Gas/Gasoline Processing, and
Petrochemical Processes in Ozone Nonattainment Areas).
which
] is subject to this division (relating to Fugitive
Emissions). Such identification must allow for ready identification of the
components, and distinction from any components
that
[
which
] are not subject to this division. The components must be identified
by one or more of the following methods:
§115.357(1) - (9)
] of this title (relating to Exemptions) do not
apply.
(VOC)
] water separators; and process drains shall be
monitored each calendar quarter (with a hydrocarbon gas analyzer).
EPA
], or any local program
with jurisdiction, the owner or operator shall demonstrate (e.g., by visual
inspection or smoke test) that the water seal controls are properly designed
and restrict ventilation.
tightly-fitting
].
which
] are unsafe to monitor
shall be identified in a list made
immediately
available upon request.
If an unsafe-to-monitor component is not considered safe to monitor within
a calendar year, then it shall be monitored as soon as possible during safe-to-monitor
times.
which
are not vented to a closed-vent system
] shall be monitored
for
fugitive leaks
each calendar quarter (with a hydrocarbon gas analyzer).
which
] has vented to the atmosphere shall be monitored
for fugitive
leaks
(with a hydrocarbon gas analyzer) and inspected within 24 hours
after actuation and the results reported in accordance with §115.786
of this title (relating to Recordkeeping Requirements).
which are
]
specified in paragraph (2) of this subsection), repair may be delayed beyond
the period designated in subsection (b) of this section for any of the following
reasons:
which
] would create
more emissions than the repair would eliminate, the repair may be delayed
until the next
scheduled process unit
shutdown, provided that:
the owner or operator complies with the requirements of §115.352(2)(A)
of this title (relating to Control Requirements); and
]
(ii)
] repair or replacement of
the component occurs at the next shutdown. The executive director, at his
discretion, may require an early process unit shutdown, or other appropriate
action, based on the number and severity of leaks awaiting a shutdown; or
which
] are not pressure
relief valves or automatic control valves, repair may only be delayed beyond
the period designated in subsection (b) of this section if:
seven days of the valve being placed on the shutdown list
]; however,
the owner or operator may keep the leaking valve on the shutdown list only
after two unsuccessful attempts to repair a leaking valve through extraordinary
efforts, provided that the second extraordinary effort attempt is made within
15 days of the first extraordinary effort attempt. For all other leaks, extraordinary
efforts shall be undertaken within
30 calendar
[
15
]
days
after the leak is found
[
of the valve being placed on
the shutdown list
], and a second extraordinary effort attempt is not
required; or
which
] demonstrates that there is a safety, mechanical,
or major environmental concern posed by repairing the leak by using "extraordinary
efforts"; or
shall
] apply.
(HRVOC)
] emissions are vented to a closed-vent system, control device,
or recovery device used to comply with the provisions of this chapter, such
system or control device
are subject to the requirements of Division
1 of this subchapter (relating to Vent Gas Control)
[
must be operating
properly
].
(4)
] Pumps, compressors, and agitators
installed on or after July 1, 2003 shall be equipped with a shaft sealing
system that prevents or detects emissions of
volatile organic compounds
[
VOC
] from the seal.
non-VOC
] barrier fluid or gas at higher pressure
than process pressure; and
EPA
] in cases where specified criteria for determining equivalency have
not been clearly identified in this section.
(5)
] The following equipment standards
shall apply to process drains.
which
] may
be used only during the period of November through February; and
(6)
] No valves shall be installed
or operated at the end of a pipe or line containing
highly-reactive volatile
organic compounds
[
HRVOC
] unless the pipe or line is sealed
with a second valve, a blind flange, or a tightly-fitting plug or cap. The
sealing device may be removed only while a sample is being taken or during
maintenance operations, and when closing the line, the upstream valve shall
be closed first.
speciated
] emissions, including
the basis for the emissions estimate.
§115.782(e)
] of this title (relating
to Procedures and Schedule for Leak Repair and Follow-up)
must
[
shall
] be maintained
.
[
and
]
Reports must
be
submitted
by January 31st and July 31st of each year
[
semiannually
] to [
the Office of Compliance and Enforcement,
]
the
Houston
[
appropriate
] regional office[
,
]
and any local air pollution control agency having jurisdiction. The report
shall contain:
(e)
] The owner or operator shall
maintain all records for at least five years and make them available for review
upon request by authorized representatives of the executive director, United
States Environmental Protection Agency, or local air pollution control agencies
with jurisdiction.
that contains
] less than 5.0% highly-reactive volatile
organic compounds by weight on an annual average basis are exempt from the
requirements of this division (relating to Fugitive Emissions), except for
§115.786(d) and (f)
[
§115.786(d) and (e)
] of this
title (relating to Recordkeeping Requirements).
§115.783(4)
]
of this title (relating to Equipment Standards):
,
] gauge (psig);
plant sites covered by a single
account number
] with less than 250 components in volatile organic
compound
[
compounds
] (VOC) service;
which
] are insulated,
making them inaccessible to monitoring with
a
[
an
] hydrocarbon
gas analyzer;
which are in compliance with
] 40 CFR §63.166(a)
and (b) (June 20, 1996); and
which are
in compliance with
] 40 CFR §63.169 (June 20, 1996).
(f)
] The following valves are exempt
from the requirements of
§115.783(5)
[
§115.352(4)
] of this title:
which
] are designed to open automatically in the event
of an emissions event;
which
] would autocatalytically polymerize or would present
an explosion, serious overpressure, or other safety hazard if capped or equipped
with a double block and bleed system; and
two
] calendar
year
[
years
], the owner or operator of the petroleum refinery;
synthetic organic chemical, polymer, resin, or methyl tert-butyl ether manufacturing
process; or natural gas/gasoline processing operation shall retain the services
of an independent third-party organization to conduct an audit of
at
least one
[
each
] process unit subject to
highly-reactive
volatile organic compound (HRVOC) monitoring in
this division
.
For accounts with greater than five process units in HRVOC service, all process
units in HRVOC service must be audited at least once every five calendar years.
The independent third-party organization must
[
(relating to Fugitive
Emissions), including
]:
which:
]
the leak/no-leak status and measured volatile organic compound (VOC) concentration
for all components for which monitoring (with a hydrocarbon gas analyzer)
or visual inspection is required that monitoring period,
] as follows
.
[
:
]
the monitoring/inspection
audit shall
] begin
after
[
when
] the owner or operator's
contracted or usual monitoring service
has completed
[
begins
] monitoring components for that monitoring period
. The audit
must be completed by the end of the monitoring period.
[
;
]
the
] following graph
must
[
shall
] be used to determine the number of components required
to be monitored in the
field survey.
[
audit out of the total
number of components in each process unit which are required to be monitored
by §115.781 of this title (relating to General Monitoring and Inspection
Requirements), based on an average of the most recent four quarters; and
]
the audit shall
] not include components
that
[
which
] were included in
the most recent field survey of that process
unit.
[
either of the most recent two audits, unless unavoidable
due to the shutdown of process units not included in either of the most recent
two audits, or for other reasons agreed upon in advance by the appropriate
regional office and any local air pollution control agency having jurisdiction;
and
]
shall
] include:
a review of the time between monitoring events
];
and
abnormal
] data patterns
indicative of failure to properly implement Test Method 21.
[
; and
]
means
] an organization
in which the owner or operator (including any subsidiary, parent company,
sister company, or joint venture) of the petroleum refinery; synthetic organic
chemical, polymer, resin, or methyl tert-butyl ether manufacturing process;
or natural gas/gasoline processing operation has no ownership or other financial
interest. If the owner or operator's routine monitoring is done by a contractor
rather than by in-house monitoring, then the independent third-party organization
must be a different contractor from that ordinarily used for those services.
appropriate
] regional office and any
local air pollution control agency having jurisdiction
that provides
the date that the independent third-party organization is scheduled to begin
the audit. The notification must be submitted at least 30 days prior to the
start date of the audit.
[
as follows:
]
Office of Compliance and Enforcement, the appropriate
] regional office[
,
] and any local air pollution control agency having jurisdiction a
copy of the results of each audit authored by the independent third-party
organization within 30 days after completion of the audit
. The report
must include:
[
, including
]
which
]
were not tagged, but [
which
] should have been tagged
in accordance
with §115.782(a) of this title
;
(3)
] the number of components monitored,
the number of leaking components, and the percentage of leaking components
identified by the independent third-party organization
during the field
survey
and by the owner or operator's contracted or usual monitoring
service in each of the following categories:
and
]
(4)
] a summary of the independent
third-party organization's review of all data generated by monitoring technicians
in the previous quarter by the owner or operator's contracted or usual monitoring
service for each of the [
following
] categories[
:
]
specified in subsection (a)(3)(A) - (C) of this section.
(e)
] Authorized representatives
of the executive director,
United States Environmental Protection Agency
[
EPA
], or any local air pollution control agency with jurisdiction
may conduct an audit of the owner or operator's leak detection and repair
program.
(f)
] In lieu of complying with subsections
(a) - (d) of this section, an owner or operator may request approval from
the executive director of an alternative method
that
[
which
] demonstrates equivalency with the independent third-party audit, provided
that the request:
which
] are
sufficient to demonstrate compliance with the alternative method; and
which
] are not required to
be monitored under Subchapter D, Division 3 of this chapter (relating to Fugitive
Emission Control in Petroleum Refining, Natural Gas/Gasoline Processing, and
Petrochemical Processes in Ozone Nonattainment Areas),
must
[
shall
] occur as soon as practicable, but no later than March 31, 2004,
except that:
shall apply
] to blind flanges, caps, or plugs at the end of a pipe or
line containing highly-reactive volatile organic compounds, sight glasses,
meters, gauges, connectors, bolted manways, heat exchanger heads, hatches,
and sump covers for which the owner or operator has notified the appropriate
regional office and any local air pollution control program with jurisdiction
that §115.781(f) of this title will be used to establish the monitoring
schedule for these components; and
shall
] be in compliance in accordance with §115.729(2) of this title
(relating to Counties and Compliance Schedules).
for at least 50% of
the process units or processes at an account as soon as practicable, but no
later than December 31, 2004. The remainder of the process units or processes
at the account that are subject to §115.788 of this title shall be audited
] as soon as practicable, but no later than December 31, 2005.
(5)
] Compliance with the recordkeeping
required by §115.786 of this title (relating to Recordkeeping Requirements)
must
[
shall
] be implemented and made available upon request
to authorized representatives of the executive director,
United States
Environmental Protection Agency
[
EPA
], or any local air pollution
control agency having jurisdiction as soon as practicable, but no later than
March 31, 2004.
(6)
] The initial monitoring of pump
seals and compressor seals using a leak definition of 500 parts per million
by volume, as required by §115.781(b)(9) of this title,
must
[
shall
] begin as soon as practicable, but no later than March 31, 2004.
Chapter 115.
CONTROL OF AIR POLLUTION FROM VOLATILE ORGANIC COMPOUNDS