National Emission Standards for Hazardous Air Pollutants: Stationary Combustion Turbines Residual Risk and Technology Review, 13524-13546 [2020-02714]
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Mark Schultz,
Delegated the authority to perform the
functions and duties of the Assistant
Secretary for Special Education and
Rehabilitative Services.
[FR Doc. 2020–04462 Filed 3–6–20; 8:45 am]
BILLING CODE 4000–01–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 63
[EPA–HQ–OAR–2017–0688; FRL–10005–14–
OAR]
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RIN 2060–AT00
National Emission Standards for
Hazardous Air Pollutants: Stationary
Combustion Turbines Residual Risk
and Technology Review
Environmental Protection
Agency (EPA).
AGENCY:
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ACTION:
Final rule.
This action finalizes the
residual risk and technology review
(RTR) conducted for the Stationary
Combustion Turbines source category
regulated under national emission
standards for hazardous air pollutants
(NESHAP). In addition, we are taking
final action addressing requirements
during periods of startup, shutdown,
and malfunction (SSM) and to add
electronic reporting requirements. The
EPA is finalizing our proposed
determination that the risks from this
source category due to emissions of air
toxics are acceptable and that the
existing NESHAP provides an ample
margin of safety to protect public health.
The EPA is also finalizing our proposed
determination that we identified no new
cost-effective controls under the
technology review that would achieve
further emissions reductions from the
source category.
DATES: This final rule is effective on
March 9, 2020. The incorporation by
reference (IBR) of certain publications
listed in the rule is approved by the
Director of the Federal Register as of
March 9, 2020.
ADDRESSES: The U.S. Environmental
Protection Agency (EPA) has established
a docket for this action under Docket ID
No. EPA–HQ–OAR–2017–0688. All
documents in the docket are listed on
the https://www.regulations.gov/
website. Although listed, some
information is not publicly available,
e.g., confidential business information
or other information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
is not placed on the internet and will be
publicly available only in hard copy
form. Publicly available docket
materials are available either
electronically through https://
www.regulations.gov/, or in hard copy at
the EPA Docket Center, WJC West
Building, Room Number 3334, 1301
Constitution Ave. NW, Washington, DC.
The Public Reading Room hours of
operation are 8:30 a.m. to 4:30 p.m.
Eastern Standard Time (EST), Monday
through Friday. The telephone number
for the Public Reading Room is (202)
566–1744, and the telephone number for
the EPA Docket Center is (202) 566–
1742.
FOR FURTHER INFORMATION CONTACT: For
questions about this final action, contact
Melanie King, Sector Policies and
Programs Division (D243–01), Office of
Air Quality Planning and Standards,
U.S. Environmental Protection Agency,
Research Triangle Park, North Carolina
27711; telephone number: (919) 541–
SUMMARY:
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2469; fax number: (919) 541–4991; and
email address: king.melanie@epa.gov.
For specific information regarding the
risk modeling methodology, contact
Mark Morris, Health and Environmental
Impacts Division (C539–02), Office of
Air Quality Planning and Standards,
U.S. Environmental Protection Agency,
Research Triangle Park, North Carolina
27711; telephone number: (919) 541–
5416; and email address: morris.mark@
epa.gov. For information about the
applicability of the Stationary
Combustion Turbines NESHAP to a
particular entity, contact Sara Ayres,
Office of Enforcement and Compliance
Assurance, U.S. Environmental
Protection Agency, 77 West Jackson
Boulevard (Mail Code E–19J), Chicago,
Illinois 60604; telephone number: (312)
353–6266; and email address:
ayres.sara@epa.gov.
SUPPLEMENTARY INFORMATION:
Preamble acronyms and
abbreviations. We use multiple
acronyms and terms in this preamble.
While this list may not be exhaustive, to
ease the reading of this preamble and for
reference purposes, the EPA defines the
following terms and acronyms here:
ANSI American National Standards
Institute
ASME American Society of Mechanical
Engineers
BACT best available control technology
CAA Clean Air Act
CAER Combined Air Emissions Reporting
CDX Central Data Exchange
CEDRI Compliance and Emissions Data
Reporting Interface
CEMS continuous emissions monitoring
systems
CFR Code of Federal Regulations
CMS continuous monitoring system
EPA Environmental Protection Agency
ERT Electronic Reporting Tool
FTIR Fourier transform infrared
HAP hazardous air pollutants(s)
HQ hazard quotient
IBR incorporation by reference
km kilometer
LAER lowest achievable emission rate
MACT maximum achievable control
technology
MIR maximum individual risk
NAICS North American Industry
Classification System
NESHAP national emission standards for
hazardous air pollutants
NOx oxides of nitrogen
NTTAA National Technology Transfer and
Advancement Act
O2 oxygen
OMB Office of Management and Budget
PB–HAP hazardous air pollutant known to
be persistent and bio-accumulative in the
environment
ppbvd parts per billion by volume, dry
basis
PRA Paperwork Reduction Act
PTC performance test code
RACT reasonably available control
technology
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RBLC RACT/BACT/LAER Clearinghouse
REL recommended exposure limit
RFA Regulatory Flexibility Act
RTR residual risk and technology review
SCR selective catalytic reduction
SSM startup, shutdown, and malfunction
TOSHI target organ-specific hazard index
tpy tons per year
UMRA Unfunded Mandates Reform Act
U.S. United States
U.S.C. United States Code
v. versus
VCS voluntary consensus standard
XML extensible markup language
Background information. On April 12,
2019, the EPA proposed the RTR for the
Stationary Combustion Turbines
NESHAP as well as amendments
addressing periods of SSM and
requiring electronic reporting. In this
action, we are finalizing certain
decisions and revisions for the rule. We
summarize some of the more significant
comments we timely received regarding
the proposed rule and provide our
responses in this preamble. A summary
of all other public comments on the
proposal and the EPA’s responses to
those comments is available in the
National Emission Standards for
Hazardous Air Pollutants from
Stationary Combustion Turbines (40
CFR part 63, subpart YYYY), Residual
Risk and Technology Review, Final
Amendments, Summary of Public
Comments and Responses on Proposed
Rule, Docket ID No. EPA–HQ–OAR–
2017–0688. A ‘‘track changes’’ version
of the regulatory language that
incorporates the changes in this action
is available in the docket.
At this time, the EPA is not finalizing
the proposed removal of the
administrative stay of the effectiveness
of the standards for new lean premix
and diffusion flame gas-fired turbines to
allow for additional time to review the
public comments on the proposed
removal of the stay, as well as a petition
to delist the Stationary Combustion
Turbines source category that was filed
in August 2019. This final rule does not
include responses to comments on
lifting the stay. The EPA is still
reviewing the comments on lifting the
stay and will respond to them in any
subsequent action.
Organization of this document. The
information in this preamble is
organized as follows:
I. General Information
A. Does this action apply to me?
B. Where can I get a copy of this document
and other related information?
C. Judicial Review and Administrative
Reconsideration
II. Background
A. What is the statutory authority for this
action?
B. What is the Stationary Combustion
Turbines source category and how does
the NESHAP regulate HAP emissions
from the source category?
C. What changes did we propose for the
Stationary Combustion Turbines source
category in our April 12, 2019, proposal?
III. What is included in this final rule?
A. What are the final rule amendments
based on the risk review for the
Stationary Combustion Turbines source
category?
B. What are the final rule amendments
based on the technology review for the
Stationary Combustion Turbines source
category?
C. What are the final rule amendments
addressing emissions during periods of
SSM?
D. What other changes have been made to
the NESHAP?
E. What are the effective and compliance
dates of the standards?
IV. What is the rationale for our final
decisions and amendments for the
Stationary Combustion Turbines source
category?
A. Residual Risk Review for the Stationary
Combustion Turbines Source Category
B. Technology Review for the Stationary
Combustion Turbines Source Category
C. SSM for the Stationary Combustion
Turbines Source Category
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D. Electronic Reporting Requirements for
the Stationary Combustion Turbines
Source Category
V. Summary of Cost, Environmental, and
Economic Impacts and Additional
Analyses Conducted
A. What are the affected facilities?
B. What are the air quality impacts?
C. What are the cost impacts?
D. What are the economic impacts?
E. What are the benefits?
F. What analysis of environmental justice
did we conduct?
G. What analysis of children’s
environmental health did we conduct?
VI. Statutory and Executive Order Reviews
A. Executive Orders 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
B. Executive Order 13771: Reducing
Regulations and Controlling Regulatory
Costs
C. Paperwork Reduction Act (PRA)
D. Regulatory Flexibility Act (RFA)
E. Unfunded Mandates Reform Act
(UMRA)
F. Executive Order 13132: Federalism
G. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
H. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
I. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
J. National Technology Transfer and
Advancement Act (NTTAA) and 1 CFR
Part 51
K. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations
L. Congressional Review Act (CRA)
I. General Information
A. Does this action apply to me?
Regulated entities. Categories and
entities potentially regulated by this
action are shown in Table 1 of this
preamble.
TABLE 1—NESHAP AND INDUSTRIAL SOURCE CATEGORIES AFFECTED BY THIS FINAL ACTION
NAICS 1 code
NESHAP and source category
Stationary Combustion Turbines ..............................................................
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1 North
2211, 486210, 211111, 211113, 221.
American Industry Classification System.
Table 1 of this preamble is not
intended to be exhaustive, but rather to
provide a guide for readers regarding
entities likely to be affected by the final
action for the source category listed. To
determine whether your facility is
affected, you should examine the
applicability criteria in the appropriate
NESHAP. If you have any questions
regarding the applicability of any aspect
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of this NESHAP, please contact the
appropriate person listed in the
preceding FOR FURTHER INFORMATION
CONTACT section of this preamble.
B. Where can I get a copy of this
document and other related
information?
In addition to being available in the
docket, an electronic copy of this final
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action will also be available on the
internet. Following signature by the
EPA Administrator, the EPA will post a
copy of this final action at: https://
www.epa.gov/stationary-sources-airpollution/stationary-combustionturbines-national-emission-standards.
Following publication in the Federal
Register, the EPA will post the Federal
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Register version and key technical
documents at this same website.
Additional information is available on
the RTR website at https://
www.epa.gov/stationary-sources-airpollution/risk-and-technology-reviewnational-emissions-standardshazardous. This information includes
an overview of the RTR program and
links to project websites for the RTR
source categories.
C. Judicial Review and Administrative
Reconsideration
Under Clean Air Act (CAA) section
307(b)(1), judicial review of the final
actions is available only by filing a
petition for review in the United States
Court of Appeals for the District of
Columbia Circuit (the court) by May 8,
2020. Under CAA section 307(b)(2), the
requirements established by this final
rule may not be challenged separately in
any civil or criminal proceedings
brought by the EPA to enforce the
requirements.
Section 307(d)(7)(B) of the CAA
further provides that only an objection
to a rule or procedure which was raised
with reasonable specificity during the
period for public comment (including
any public hearing) may be raised
during judicial review. This section also
provides a mechanism for the EPA to
reconsider the rule if the person raising
an objection can demonstrate to the
Administrator that it was impracticable
to raise such objection within the period
for public comment or if the grounds for
such objection arose after the period for
public comment (but within the time
specified for judicial review) and if such
objection is of central relevance to the
outcome of the rule. Any person seeking
to make such a demonstration should
submit a Petition for Reconsideration to
the Office of the Administrator, U.S.
EPA, Room 3000, EPA WJC South
Building, 1200 Pennsylvania Ave. NW,
Washington, DC 20460, with a copy to
both the person(s) listed in the
preceding FOR FURTHER INFORMATION
CONTACT section, and the Associate
General Counsel for the Air and
Radiation Law Office, Office of General
Counsel (Mail Code 2344A), U.S. EPA,
1200 Pennsylvania Ave. NW,
Washington, DC 20460.
II. Background
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A. What is the statutory authority for
this action?
Section 112 of the CAA establishes a
two-stage regulatory process to address
emissions of hazardous air pollutants
(HAP) from stationary sources. In the
first stage, we must identify categories
of sources emitting one or more of the
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HAP listed in CAA section 112(b) and
then promulgate technology-based
NESHAP for those sources. ‘‘Major
sources’’ are those that emit, or have the
potential to emit, any single HAP at a
rate of 10 tons per year (tpy) or more,
or 25 tpy or more of any combination of
HAP. For major sources, these standards
are commonly referred to as maximum
achievable control technology (MACT)
standards and must reflect the
maximum degree of emission reductions
of HAP achievable (after considering
cost, energy requirements, and non-air
quality health and environmental
impacts). In developing MACT
standards, CAA section 112(d)(2) directs
the EPA to consider the application of
measures, processes, methods, systems,
or techniques, including, but not limited
to those that reduce the volume of or
eliminate HAP emissions through
process changes, substitution of
materials, or other modifications;
enclose systems or processes to
eliminate emissions; collect, capture, or
treat HAP when released from a process,
stack, storage, or fugitive emissions
point; are design, equipment, work
practice, or operational standards; or
any combination of the above.
For these MACT standards, the statute
specifies certain minimum stringency
requirements, which are referred to as
MACT floor requirements, and which
may not be based on cost
considerations. See CAA section
112(d)(3). For new sources, the MACT
floor cannot be less stringent than the
emission control achieved in practice by
the best-controlled similar source. The
MACT standards for existing sources
can be less stringent than floors for new
sources, but they cannot be less
stringent than the average emission
limitation achieved by the bestperforming 12 percent of existing
sources in the category or subcategory
(or the best-performing five sources for
categories or subcategories with fewer
than 30 sources). In developing MACT
standards, we must also consider
control options that are more stringent
than the floor under CAA section
112(d)(2). We may establish standards
more stringent than the floor, based on
the consideration of the cost of
achieving the emissions reductions, any
non-air quality health and
environmental impacts, and energy
requirements.
In the second stage of the regulatory
process, the CAA requires the EPA to
undertake two different analyses, which
we refer to as the technology review and
the residual risk review. Under the
technology review, we must review the
technology-based standards and revise
them ‘‘as necessary (taking into account
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developments in practices, processes,
and control technologies)’’ no less
frequently than every 8 years, pursuant
to CAA section 112(d)(6). Under the
residual risk review, we must evaluate
the risk to public health remaining after
application of the technology-based
standards and revise the standards, if
necessary, to provide an ample margin
of safety to protect public health or to
prevent, taking into consideration costs,
energy, safety, and other relevant
factors, an adverse environmental effect.
The residual risk review is required
within 8 years after promulgation of the
technology-based standards, pursuant to
CAA section 112(f). In conducting the
residual risk review, if the EPA
determines that the current standards
provide an ample margin of safety to
protect public health, it is not necessary
to revise the MACT standards pursuant
to CAA section 112(f).1 For more
information on the statutory authority
for this rule, see 84 FR 15046.
B. What is the Stationary Combustion
Turbines source category and how does
the NESHAP regulate HAP emissions
from the source category?
The EPA promulgated the Stationary
Combustion Turbines NESHAP on
March 5, 2004 (69 FR 10512). The
standards are codified at 40 CFR part 63,
subpart YYYY, and apply to stationary
combustion turbines at major sources of
HAP. The stationary combustion turbine
industry consists of facilities that own
and operate stationary combustion
turbines. The source category covered
by this MACT standard currently
includes 243 facilities. Stationary
combustion turbines are typically
located at power plants, compressor
stations, landfills and industrial
facilities such as chemical plants.
Stationary combustion turbines have
been divided into the following eight
subcategories: (1) Emergency stationary
combustion turbines, (2) stationary
combustion turbines which burn
landfill or digester gas equivalent to 10
percent or more of the gross heat input
on an annual basis or where gasified
municipal solid waste is used to
generate 10 percent or more of the gross
heat input to the stationary combustion
turbine on an annual basis, (3)
stationary combustion turbines of less
than 1 megawatt rated peak power
output, (4) stationary lean premix
combustion turbines when firing gas
1 The court has affirmed this approach of
implementing CAA section 112(f)(2)(A): NRDC v.
EPA, 529 F.3d 1077, 1083 (DC Cir. 2008) (‘‘If EPA
determines that the existing technology-based
standards provide an ‘ample margin of safety,’ then
the Agency is free to readopt those standards during
the residual risk rulemaking.’’).
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and when firing oil at sites where all
turbines fire oil no more than an
aggregate total of 1,000 hours annually
(also referred to herein as ‘‘lean premix
gas-fired turbines’’), (5) stationary lean
premix combustion turbines when firing
oil at sites where all turbines fire oil
more than an aggregate total of 1,000
hours annually (also referred to herein
as ‘‘lean premix oil-fired turbines’’), (6)
stationary diffusion flame combustion
turbines when firing gas and when
firing oil at sites where all turbines fire
oil no more than an aggregate total of
1,000 hours annually (also referred to
herein as ‘‘diffusion flame gas-fired
turbines’’), (7) stationary diffusion flame
combustion turbines when firing oil at
sites where all turbines fire oil more
than an aggregate total of 1,000 hours
annually (also referred to herein as
‘‘diffusion flame oil-fired turbines’’),
and (8) stationary combustion turbines
operated on the North Slope of Alaska
(defined as the area north of the Arctic
Circle (latitude 66.5 degrees North)).
The sources of emissions are the
exhaust gases from combustion of
gaseous and liquid fuels in a stationary
combustion turbine. The HAP that are
present in the exhaust gases from
stationary combustion turbines include
formaldehyde, toluene, benzene, and
acetaldehyde. Metallic HAP are present
in the exhaust from distillate oil-fired
turbines; these metallic HAP are
generally carried over from the fuel
constituents.
The NESHAP requires new or
reconstructed stationary combustion
turbines in the lean premix gas-fired,
lean premix oil-fired, diffusion flame
gas-fired, and diffusion flame oil-fired
subcategories to meet a formaldehyde
limit of 91 parts per billion by volume,
dry basis (ppbvd) at 15-percent oxygen
(O2). Compliance is demonstrated
through initial and annual performance
testing and continuous monitoring of
operating parameters. The requirements
of the rule are currently under a stay of
effectiveness for new lean premix and
diffusion flame gas-fired turbines.
C. What changes did we propose for the
Stationary Combustion Turbines source
category in our April 12, 2019,
proposal?
On April 12, 2019, the EPA published
a proposed rule in the Federal Register
for the Stationary Combustion Turbines
NESHAP, 40 CFR part 63, subpart
YYYY, that took into consideration the
RTR analyses. In the proposed rule, we
proposed to find that risks from the
Stationary Combustion Turbines source
category due to emissions of air toxics
are acceptable and that the existing
NESHAP provides an ample margin of
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safety to protect public health. No new
cost-effective controls were identified in
the technology review for the proposed
rule. The EPA also proposed to
eliminate the exemption for periods of
SSM, and our risk analysis assumed
removal of that exemption. We
proposed a new requirement to
electronically submit performance test
results and semiannual compliance
reports. Finally, we proposed to remove
the stay of the standards for new lean
premix and diffusion flame gas-fired
turbines. We did not propose any
revisions to the emission standards
based on our RTR.
III. What is included in this final rule?
This action finalizes the EPA’s
determinations pursuant to the RTR
provisions of CAA section 112 for the
Stationary Combustion Turbines source
category. This action also finalizes other
changes to the NESHAP, including
amendments to the SSM provisions and
the addition of electronic reporting
requirements. This action reflects
changes to the April 19, 2019, proposal
in consideration of comments received
during the public comment period
described in section IV of this preamble.
As stated previously, the EPA is not
finalizing the proposed removal of the
stay of the effectiveness of the standards
for new lean premix and diffusion flame
gas-fired turbines at this time. The EPA
received numerous comments on the
proposed stay indicating that 180 days
is not sufficient time for owners and
operators to conduct all of the activities
that are needed for their turbines to
come into compliance with the
standards, which include the design,
procurement, and installation of
emission controls and parametric
monitoring equipment that can fit
within existing sites (as compared to
new facilities where the controls are
incorporated into the facility design),
performance testing, and
implementation of procedures for
monitoring, recordkeeping, and
reporting. More time is needed to
review these comments on the removal
of the stay. In addition, the EPA
received a petition to delist the
Stationary Combustion Turbines source
category from regulation under CAA
section 112 in August 2019. As
discussed in more detail in the April 12,
2019, proposal, the EPA proposed to
delist certain subcategories of stationary
combustion turbines in 2004 under CAA
section 112(c)(9)(B) and stayed the
effectiveness of the standards for those
subcategories, pending the outcome of
the proposed delisting. A subsequent
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2007 decision by the court 2 held that
the EPA has no authority to delist
subcategories under CAA section
112(c)(9)(B). Consequently, the EPA
proposed to remove the stay in the April
12, 2019, proposal. In recognition of the
EPA’s inability to delist subcategories
under CAA section 112(c)(9)(B), the new
August 2019 petition requests delisting
of the entire Stationary Combustion
Turbines source category and provides
an assessment of the risks for the entire
source category. A copy of the petition
is in the docket for this rulemaking
(Docket ID No. EPA–HQ–OAR–2017–
0688). The EPA is in the process of
reviewing the petition and has not made
a determination regarding whether the
information included in the petition
supports delisting the entire source
category, but notes that the petitioners
provided an analysis of the risks from
the source category and, based on their
analysis, the petitioners concluded that
a demonstration can be made that
delisting is appropriate under CAA
section 112(c)(9)(B). The EPA has
determined that it would be reasonable
to delay taking final action on the stay
until we have made a determination
regarding the source category delisting
petition, so that turbine owners and
operators do not make expenditures on
emission controls and performance
testing that will not be required if the
source category is delisted. Such
expenditures would be wasteful and
unwarranted if the source category is
delisted. Moreover, the EPA has no legal
obligation to lift the stay in this RTR
rulemaking. Although the EPA often
uses the RTR rulemaking vehicle to
revise or update various aspects of a
NESHAP, as it did here with respect to
its proposal to eliminate a stay
provision in the rule, the EPA did not
do so nor is the EPA required to do so
under CAA section 112(d)(6) or (f)(4).
A. What are the final rule amendments
based on the risk review for the
Stationary Combustion Turbines source
category?
We are finalizing our proposed
finding that risks remaining after
implementation of the existing MACT
standards for this source category (as
revised in this action to remove the SSM
exemption) are acceptable. We are also
finalizing our proposed determination
that the current NESHAP (as revised in
this action to remove the SSM
exemption) provides an ample margin of
safety to protect public health.
Therefore, we are not finalizing any
revisions to the numerical emission
2 NRDC
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limits based on these analyses
conducted under CAA section 112(f).
B. What are the final rule amendments
based on the technology review for the
Stationary Combustion Turbines source
category?
We determined that there are no
developments in practices, processes,
and control technologies that warrant
revisions to the MACT standards for this
source category. Therefore, we are not
finalizing revisions to the MACT
standards under CAA section 112(d)(6).
C. What are the final rule amendments
addressing emissions during periods of
SSM?
In its 2008 decision in Sierra Club v.
EPA, 551 F.3d 1019 (D.C. Cir. 2008), the
court vacated portions of two provisions
in the EPA’s CAA section 112
regulations governing the emissions of
HAP during periods of SSM.
Specifically, the court vacated the SSM
exemption contained in 40 CFR
63.6(f)(1) and 40 CFR 63.6(h)(1), holding
that under section 302(k) of the CAA,
emissions standards or limitations must
be continuous in nature and that the
SSM exemption violates the CAA’s
requirement that some CAA section 112
standards apply continuously.
We have eliminated the SSM
exemption in this rule. Consistent with
Sierra Club v. EPA, the EPA has
established standards in this rule that
apply at all times. We have also revised
Table 7 (the General Provisions
applicability table) in several respects as
is explained in more detail in the
proposal. For example, we have
eliminated the incorporation of the
General Provisions’ requirement that the
source develop an SSM plan. We have
also eliminated and revised certain
recordkeeping and reporting
requirements that are related to the SSM
exemption as described in detail in the
proposed rule and in section IV.C of this
preamble.
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D. What other changes have been made
to the NESHAP?
The EPA is requiring owners and
operators of stationary combustion
turbine facilities to submit electronic
copies of certain required performance
test results and semiannual compliance
reports through the EPA’s Central Data
Exchange (CDX) using the Compliance
and Emissions Data Reporting Interface
(CEDRI). The final rule requires that
performance test results collected using
test methods that are supported by the
EPA’s Electronic Reporting Tool (ERT)
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as listed on the ERT website 3 at the time
of the test be submitted in the format
generated through the use of the ERT
and that other performance test results
be submitted in portable document
format using the attachment module of
the ERT. The test methods required by
40 CFR part 63, subpart YYYY that are
currently supported by the ERT are EPA
Methods 3A and 4 of 40 CFR part 60,
appendix A. For periodic compliance
reports, the final rule requires that
owners and operators use the
appropriate spreadsheet template to
submit information to CEDRI. The final
version of the template for these reports
is located on the CEDRI website.4
The electronic submittal of the reports
addressed in this rulemaking will
increase the usefulness of the data
contained in those reports, is in keeping
with current trends in data availability
and transparency, will further assist in
the protection of public health and the
environment, will improve compliance
by facilitating the ability of regulated
facilities to demonstrate compliance
with requirements and by facilitating
the ability of delegated state, local,
tribal, and territorial air agencies and
the EPA to assess and determine
compliance, and will ultimately reduce
burden on regulated facilities, delegated
air agencies, and the EPA. Electronic
reporting also eliminates paper-based,
manual processes, thereby saving time
and resources, simplifying data entry,
eliminating redundancies, minimizing
data reporting errors, and providing data
quickly and accurately to the affected
facilities, air agencies, the EPA, and the
public. For a more thorough discussion
of electronic reporting, see the
memorandum, Electronic Reporting
Requirements for New Source
Performance Standards (NSPS) and
National Emission Standards for
Hazardous Air Pollutants (NESHAP)
Rules, available in Docket ID No. EPA–
HQ–OAR–2017–0688.
E. What are the effective and
compliance dates of the standards?
The revisions to the MACT standards
being promulgated in this action are
effective on March 9, 2020. The
compliance date for affected sources to
comply with the amendments
pertaining to SSM and electronic
reporting is 180 days after the effective
date of the final rule. As discussed
elsewhere in this preamble, we are
adding a requirement that performance
test results and semiannual compliance
3 https://www.epa.gov/electronic-reporting-airemissions/electronic-reporting-tool-ert.
4 https://www.epa.gov/electronic-reporting-airemissions/compliance-and-emissions-datareporting-interface-cedri.
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reports be submitted electronically, and
we are changing the requirements for
periods of SSM by removing the
exemption from the requirement to meet
the emission standards during periods
of SSM and promulgating an operational
standard for startup. Our experience
with similar industries that are required
to convert reporting mechanisms to
install necessary hardware and software,
become familiar with the process of
submitting performance test results and
compliance reports electronically
through the EPA’s CEDRI, test these new
electronic submission capabilities, and
reliably employ electronic reporting
shows that a time period of a minimum
of 90 days and, more typically, 180
days, is generally necessary to
successfully accomplish these revisions.
Our experience with similar industries
further shows that this sort of regulated
facility generally requires a time period
of 180 days to read and understand the
amended rule requirements; to evaluate
their operations to ensure that they can
meet the standards during periods of
startup and shutdown as defined in the
rule and make any necessary
adjustments; and to update their
operation, maintenance, and monitoring
plans to reflect the revised
requirements. The EPA recognizes the
confusion that multiple different
compliance dates for individual
requirements would create and the
additional burden such an assortment of
dates would impose. From our
assessment of the timeframe needed for
compliance with the entirety of the
revised requirements, the EPA considers
a period of 180 days to be the most
expeditious compliance period
practicable and, thus, is requiring that
affected sources must be in compliance
with all of the revised requirements
within 180 days of the regulation’s
effective date. All affected facilities
would have to continue to meet the
current requirements of 40 CFR part 63,
subpart YYYY, until the applicable
compliance date of the amended rule.
IV. What is the rationale for our final
decisions and amendments for the
Stationary Combustion Turbines source
category?
For each issue, this section provides
a description of what we proposed and
what we are finalizing for the issue, the
EPA’s rationale for the final decisions
and amendments, and a summary of key
comments and responses. For all
comments not discussed in this
preamble, comment summaries and the
EPA’s responses can be found in the
comment summary and response
document available in the docket.
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A. Residual Risk Review for the
Stationary Combustion Turbines Source
Category
in the residual risk technical support
document, Residual Risk Assessment for
the Stationary Combustion Turbines
Source Category in Support of the 2019
Risk and Technology Review Proposed
Rule, available in the docket for this
rulemaking (Docket ID No. EPA–HQ–
OAR–2017–0688).
and presented the results of this review,
along with our proposed decisions
regarding risk acceptability and ample
margin of safety, in the April 12, 2019,
proposed rule for 40 CFR part 63,
subpart YYYY (84 FR 15046). The
results of the risk assessment for the
proposal are presented briefly below in
Table 2 of this preamble. More detail is
1. What did we propose pursuant to
CAA section 112(f) for the Stationary
Combustion Turbines source category?
Pursuant to CAA section 112(f), the
EPA conducted a residual risk review
13529
TABLE 2—STATIONARY COMBUSTION TURBINES INHALATION RISK ASSESSMENT RESULTS
Maximum individual
cancer risk
(in 1 million) 2
Number of
facilities 1
Population at
increased risk of
cancer ≥1-in-1 million
Based on . . .
Based on . . .
Annual cancer
incidence
(cases per year)
Based on . . .
Maximum chronic
noncancer
TOSHI 3
Based on . . .
Actual
emissions
level
Allowable
emissions
level
Actual
emissions
level
Allowable
emissions
level
Actual
emissions
level
Allowable
emissions
level
Actual
emissions
level
Allowable
emissions
level
3
3
42,000
42,000
0.04
0.04
0.04
0.04
253
Maximum
screening acute
noncancer HQ 4
Based on actual emissions level
HQREL = 2 (acrolein), HQAEGL–1 = 0.07
1 Number
of facilities evaluated in the risk analysis.
individual excess lifetime cancer risk due to HAP emissions from the source category.
target organ specific hazard index (TOSHI). The target organ system with the highest TOSHI for the source category is respiratory. The respiratory
TOSHI was calculated using the California Environmental Protection Agency chronic recommended exposure limit (REL) for acrolein. The EPA is in the process of
updating the Integrated Risk Information System reference concentration for acrolein.
4 The maximum estimated acute exposure concentration was divided by available short-term threshold values to develop an array of hazard quotient (HQ) values.
HQ values shown use the lowest available acute threshold value, which in most cases is the REL. When an HQ exceeds 1, we also show the HQ using the next lowest available acute dose-response value.
2 Maximum
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3 Maximum
The results of the proposal inhalation
risk modeling using actual and
allowable emissions data, as shown in
Table 2 of this preamble, indicate that
the maximum lifetime individual cancer
risk (MIR) is 3-in-1 million, the
maximum chronic noncancer TOSHI is
0.04, and the maximum screening acute
noncancer HQ (off-facility site) is 2
(driven by acrolein). Only one facility
has an HQ (REL) that exceeds 1. At
proposal, the total annual cancer
incidence (national) from these facilities
was estimated to be 0.04 excess cancer
cases per year, or one case in every 25
years. The facility-wide maximum
lifetime cancer MIR was estimated to be
2,000-in-1 million at proposal, driven by
ethylene oxide emissions from chemical
manufacturing. At proposal, the total
estimated cancer incidence from whole
facility emissions was estimated to be
0.7 excess cancer cases per year, or one
excess case in every 1 to 2 years.
Approximately 2.8 million people were
estimated to have cancer risks above 1in-1 million from exposure to HAP
emitted from both MACT and nonMACT sources at the facilities in the
source category. The estimated
maximum chronic noncancer TOSHI
based on facility-wide emissions is 4
(respiratory), driven by emissions of
chlorine from chemical manufacturing,
and approximately 360 people are
exposed to a TOSHI above 1.
At proposal, potential multipathway
human health risks were estimated
using a three-tier screening assessment
of the persistent bio-accumulative HAP
(PB–HAP) emitted by facilities in this
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source category. The only pollutants
with elevated Tier 1 and Tier 2
screening values were arsenic (cancer),
cadmium (noncancer), and mercury
(noncancer). The Tier 3 screening values
for these pollutants were low. For
cancer, the Tier 3 screening value for
arsenic was 4. For noncancer, the Tier
3 screening value for cadmium was less
than 1, and the screening value for
mercury was 1.
Several environmental HAP are
emitted by sources within this source
category: Arsenic, dioxins/furans, and
polycyclic organic matter. Therefore, at
proposal we conducted a three-tier
screening assessment of the potential
adverse environmental risks associated
with emissions of these pollutants.
Based on this assessment (through Tier
2), there were no exceedances of any of
the ecological benchmarks evaluated for
any of the pollutants, and we proposed
that we do not expect an adverse
environmental effect as a result of HAP
emissions from this source category.
We weighed all health risk factors,
including those shown in Table 2 of this
preamble, in our risk acceptability
determination and proposed that the
residual risks from the Stationary
Combustion Turbines source category
are acceptable (section IV.B.1 of
proposal preamble, 84 FR 15062, April
12, 2019). We then considered whether
40 CFR part 63, subpart YYYY provides
an ample margin of safety to protect
public health and prevents, taking into
consideration costs, energy, safety, and
other relevant factors, an adverse
environmental effect. In considering
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whether the standards should be
tightened to provide an ample margin of
safety to protect public health, we
considered all health factors evaluated
in the risk assessment and evaluated the
cost and feasibility of available control
technologies and other measures
(including the controls, measures, and
costs reviewed under the technology
review) that could be applied to this
source category to further reduce the
risks (or potential risks) due to
emissions of HAP identified in our risk
assessment. In this analysis, we
considered the results of the technology
review, risk assessment, and other
aspects of our MACT rule review to
determine whether there are any
emission reduction measures necessary
to provide an ample margin of safety
with respect to the risks associated with
these emissions. Our risk analysis
indicated the risks from the source
category are low for both cancer and
noncancer health effects, and, therefore,
any risk reductions from further
available control options would result
in minimal health benefits. Moreover, as
noted in our discussion of the
technology review, no additional costeffective measures were identified for
reducing HAP emissions from affected
sources in the Stationary Combustion
Turbines source category. Thus, we
determined that the current Stationary
Combustion Turbines NESHAP provides
an ample margin of safety to protect
public health.
Our technology review focused on
identifying developments in practices,
processes, and control technologies that
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have occurred since the Stationary
Combustion Turbines NESHAP was
originally promulgated in 2004. Our
review of the developments in
technology for the Stationary
Combustion Turbines source category
did not reveal any changes that require
revisions to the emission standards. The
only add-on HAP emission control
technology identified in the original
NESHAP rulemaking was an oxidation
catalyst. No new or improved add-on
control technologies that reduce HAP
emissions from turbines were identified
during the technology review. Our
review also did not identify any new or
improved operation and maintenance
practices, process changes, pollution
prevention approaches, or testing and
monitoring techniques for stationary
combustion turbines. Therefore, we
determined that no revisions are
necessary pursuant to CAA section
112(d)(6).
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2. How did the risk review change for
the Stationary Combustion Turbines
source category?
The only change in the risk
assessment for the final rule is that the
EPA modeled an additional 46 turbines
that were identified in a public
comment (Docket ID Item No. EPA–HQ–
OAR–2017–0688–0116) as subject to the
Stationary Combustion Turbines
NESHAP. The emissions data used to
model those additional turbines and the
results of the modeling are discussed in
the memorandum titled Emissions Data
Used in Modeling Files for Additional
Turbines for Stationary Combustion
Turbines Risk and Technology Review
(RTR), which is in the docket for this
rulemaking (Docket ID No. EPA–HQ–
OAR–2017–0688). The modeling input
files are also available in the docket.
The risks for the additional turbines
were all lower than the risks for the
turbines modeled for the proposed rule,
so the additional risk analysis did not
result in changes to our proposed
decisions on risk acceptability, ample
margin of safety, and adverse
environmental effect.
3. What key comments did we receive
on the risk review, and what are our
responses?
We received comments in support of
and against the proposed residual risk
review and our determination that no
revisions were warranted under CAA
section 112(f)(2) for the Stationary
Combustion Turbines source category.
Generally, the comments that were not
supportive of the determination from
the risk review suggested changes to the
underlying risk assessment
methodology. For example, some
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commenters stated that the EPA should
lower the acceptability benchmark so
that risks below 100-in-1 million are
unacceptable, include emissions outside
of the source categories in question in
the risk assessment, and assume that
pollutants with noncancer health risks
have no safe level of exposure. After
review of all the comments received, we
determined that no changes were
necessary. The comments and our
specific responses can be found in the
document, National Emission Standards
for Hazardous Air Pollutants from
Stationary Combustion Turbines (40
CFR part 63, subpart YYYY) Residual
Risk and Technology Review, Final
Amendments: Summary of Public
Comments and Responses on Proposed
Rule, available in the docket for this
action (Docket ID No. EPA–HQ–OAR–
2017–0688).
4. What is the rationale for our final
approach and final decisions for the risk
review?
As noted in our proposal, the EPA
sets standards under CAA section
112(f)(2) using a two-step standardsetting approach, with an analytical first
step to make a risk-acceptability
determination that considers all health
information, including risk estimation
uncertainty, and includes a presumptive
limit on MIR of approximately 1-in-10
thousand (see 54 FR 38045, September
14, 1989). We weigh all health risk
factors in our risk acceptability
determination, including the cancer
MIR, cancer incidence, the maximum
cancer TOSHI, the maximum acute
noncancer HQ, the extent of noncancer
risks, the distribution of cancer and
noncancer risks in the exposed
population, and the risk estimation
uncertainties.
Since proposal, neither the risk
assessment nor our determinations
regarding risk acceptability, ample
margin of safety, or adverse
environmental effects have changed,
even considering the additional 46
turbines modeled. Therefore, for the
reasons explained in the proposed rule,
we determined that the risks from this
source category are acceptable, and the
current standards provide an ample
margin of safety to protect public health
and prevent an adverse environmental
effect. Therefore, we are not revising
this subpart to require additional
controls pursuant to CAA section
112(f)(2) based on the residual risk
review, and we are readopting the
existing standards under CAA section
112(f)(2).
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B. Technology Review for the Stationary
Combustion Turbines Source Category
1. What did we propose pursuant to
CAA section 112(d)(6) for the Stationary
Combustion Turbines source category?
Pursuant to CAA section 112(d)(6), we
conducted a technology review, which
focused on identifying and evaluating
developments in practices, processes,
and control technologies for control of
HAP emissions from stationary
combustion turbines. No cost-effective
developments in practices, processes, or
control technologies were identified in
our technology review to warrant
revisions to the standards. More
information concerning our technology
review can be found in the Technology
Review for Stationary Combustion
Turbines Risk and Technology Review
(RTR) memorandum, which is in the
docket for this action (Docket ID No.
EPA–HQ–OAR–2017–0688), and in the
preamble for the proposed rule (84 FR
15046).
2. How did the technology review
change for the Stationary Combustion
Turbines source category?
The technology review has not
changed since the proposal.
3. What key comments did we receive
on the technology review, and what are
our responses?
We received both supportive and
adverse comments on the proposed
technology review. Most commenters
supported the EPA’s proposed
technology review determination. The
summarized comments and the EPA’s
responses are provided in the National
Emission Standards for Hazardous Air
Pollutants from Stationary Combustion
Turbines (40 CFR part 63, subpart
YYYY), Residual Risk and Technology
Review, Final Amendments, Summary
of Public Comments and Responses on
Proposed Rule document referenced in
section IV.A.3 of the preamble. The
most significant adverse comments and
the EPA’s responses are also provided
below.
Comment: One commenter stated that
the EPA reviewed only the technology
used to limit formaldehyde in the
technology review and does not
evaluate selective catalytic reduction
(SCR) or any other of the technologies
identified as ‘‘developments’’ within the
meaning of CAA section 112(d)(6),
which is unlawful and arbitrary.
The commenter stated that the EPA
ignored other HAP controls in the
technology review—such as wet
controls (water or steam injection), lean
premixed combustion, and SCR—
without any rational explanation. The
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commenter noted that the EPA is aware
of evidence showing that SCR can and
does reduce HAP, such as benzene. The
commenter cited a 2016 study, Catalytic
Destruction of a Surrogate Organic
Hazardous Air Pollutant as a Potential
Co-benefit for Coal-fired Selective
Catalyst Reduction Systems (C.W. Lee et
al.), which found that ‘‘significant
destruction of benzene occurred under a
broad range of SCR operating
conditions, suggesting that a large
number of coalfired utility boilers
which are equipped with SCR for NOX
control have potential to achieve
reduction of organic HAP emissions as
a co-benefit.’’
The commenter stated that the EPA
must consider ways to reduce emissions
through developments such as: Methods
to assure more efficient use of turbines;
use of lower HAP fuels; and/or
alternative energy generation altogether
through renewables and/or battery
storage systems. According to the
commenter, the EPA must consider
battery storage in particular because this
has the potential to increase efficiency
and reduce emissions, and to reduce all
of the turbine-based risks the EPA found
to zero by reducing the emissions
completely if paired with a renewable
energy source such as solar. The
commenter stated that the EPA does not
evaluate or take into account any of
these developments, and this is
unlawful, arbitrary, and capricious
under CAA section 112(d)(6).
The commenter noted that there are
also developments in volatile organic
compounds, acid gas, and metal
controls, leak detection and repair, and
monitoring that the EPA must consider
and ensure that the standards ‘‘tak[e]
into account’’ for this source category
and these facilities. The commenter
stated that since the EPA finalized the
original standards, the EPA has
recognized such developments in other
contexts. The commenter concluded
that the EPA would violate CAA section
112(d)(6) by failing to consider and
account for the ‘‘developments’’ in
fenceline monitoring, leak detection and
repair, and pollution controls—
particularly where data show significant
health risks from a range of emitted
pollutants, including cancer, chronic
noncancer, and acute risk. The
commenter stated that refusing to
consider these developments is also
arbitrary. The commenter explained that
many facilities that include turbines are
similar to refineries, in their significant
potential for leaks and emission spikes
that cause health and safety threats, and
in their complexity. The commenter
concluded that all of the developments
discussed are readily available, would
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improve emission control, reduce health
risks and refusing to consider them and
revise the standards to ‘‘account’’ for
them would be unlawful and arbitrary.
Conversely, another commenter stated
that, setting aside whether fenceline
monitoring technology constitutes a
‘‘development’’ under CAA section
112(d)(6), it would be arbitrary and
capricious to adopt fenceline
monitoring requirements for stationary
combustion turbines as part of this RTR.
Fenceline monitoring is used to identify
sources of fugitive emissions. According
to the commenter, stationary
combustion turbines do not have
fugitive HAP emissions. According to
the commenter, even if some
combustion turbine facilities may also
contain other equipment with the
potential for fugitive emissions, such as
natural gas transmission pipelines, that
other equipment is not part of the
source category under review here and
cannot be the basis for new
requirements adopted pursuant to CAA
section 112(d)(6) review for combustion
turbines.
Response: The EPA disagrees with the
commenter that it only reviewed
technologies used to limit formaldehyde
emissions. As discussed in the
memorandum, Technology Review for
Stationary Combustion Turbines Risk
and Technology Review (RTR) (Docket
ID Item No. EPA–HQ–OAR–2017–0688–
0066), the EPA reviewed a variety of
sources of information during the
technology review. Those sources of
information included the EPA’s RACT/
BACT/LAER Clearinghouse (RBLC),
construction and operating permits for
stationary combustion turbines,
information provided by owners and
operators of stationary combustion
turbines, and manufacturers of emission
control technologies and testing
equipment. The review was not limited
to technologies that limit formaldehyde
emissions, as evidenced by the RBLC
search criteria documented in Appendix
A of the memorandum and the
questions asked of industry stakeholders
described in Appendix B of the
memorandum.
The 2016 study cited by the
commenter as evidence that SCR
reduces HAP such as benzene evaluated
the HAP reductions from SCR applied to
simulated coal combustion flue gases.
The chemical composition of the coal
combustion flue gases is very different
from the chemical composition of the
exhaust from stationary combustion
turbines, and there is no evidence
provided that the use of SCR in coal
combustion exhaust and the resulting
catalytic chemical reactions that cause
the destruction of benzene would occur
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13531
in the same way if SCR is applied to
stationary combustion turbines. The
information provided to the EPA
regarding ‘‘dual-purpose’’ catalysts that
include SCR for nitrogen oxides (NOx)
removal and oxidation for carbon
monoxide (CO) and HAP removal
indicates that the HAP reduction occurs
due to the oxidation and not from the
SCR.5 The commenter did not provide
any evidence that water or steam
injection would reduce HAP emissions,
or that fuels that lead to lower HAP
emissions have been developed. Lean
premix combustion is not a new
technology (and is one of the
subcategories established in the original
2004 40 CFR part 63, subpart YYYY
rulemaking) and the commenter did not
provide any evidence that there have
been any developments in the
technology. As discussed in the
memorandum cited above, the trade
organization representing gas turbine
manufacturers indicated that there have
not been any changes in turbine design
since the 2004 rulemaking. We disagree
that the EPA must consider alternative
energy generation altogether through
renewables and/or battery storage and
that the use of batteries if paired with
renewable energy such as solar would
reduce emissions completely. The
commenter’s suggested technology
(renewables and batteries) is not a
revision to the emissions standard for
the Stationary Combustion Turbines
source category, which is what the EPA
is required to review and revise as
appropriate, under CAA section
112(d)(6). The commenter is suggesting
elimination of combustion turbines as a
source category and that is beyond the
scope of this rulemaking. Even if such
an approach were an appropriate
‘‘revision’’ of the emission standards for
combustion turbines under CAA section
112(d)(6), the commenter did not
provide any information to show that
using renewables or battery storage has
been demonstrated on the scale that
would be needed to replace the
generation produced by the combustion
turbines subject to subpart YYYY.
Regarding the comment that the EPA
should consider leak detection and
repair and fenceline monitoring
requirements, the EPA notes that those
requirements were included in the
NESHAP for Petroleum Refineries (40
CFR part 63, subpart CC). Those
requirements for refineries target
refinery MACT-regulated fugitive
emission sources (e.g., storage tanks,
5 See the memorandum, Technology Review for
Stationary Combustion Turbines Risk and
Technology Review (RTR) (Docket ID Item No. EPA–
HQ–OAR–2017–0688–0066).
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equipment leaks, and wastewater).
Fenceline monitoring, as discussed in
the preamble to the proposed Petroleum
Refinery rule (79 FR 36920), may
identify significant increases in
emissions, but small increases in
emissions are unlikely to impact the
fenceline concentrations. Fenceline
monitoring would not be beneficial for
the Stationary Combustion Turbines
source category because stationary
turbines have very low fugitive HAP
emissions and their operation does not
involve storage and transport of large
volumes of volatile organic materials
unlike the refinery sector. The potential
for fugitive volatile organic HAP
emissions, as a result of the reduced
amount of transport and the reduced
storage of volatile organic materials, is
vastly lower.
4. What is the rationale for our final
approach for the technology review?
We evaluated all of the comments on
the EPA’s technology review and
determined that no changes to the
review are needed based on the
comments. For the reasons explained in
the proposed rule, we determined that
no cost-effective developments in
practices, processes, or control
technologies were identified in our
technology review to warrant revisions
to the standards. More information
concerning our technology review and
how we evaluate cost effectiveness can
be found in the Technology Review for
Stationary Combustion Turbines Risk
and Technology Review (RTR)
memorandum, which is in the docket
for this action (Docket ID No. EPA–HQ–
OAR–2017–0688), and in the preamble
for the proposed rule (84 FR 15046).
Therefore, pursuant to CAA section
112(d)(6), we are finalizing our
technology review as proposed.
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C. SSM Provisions for the Stationary
Combustion Turbines Source Category
1. What did we propose for the
Stationary Combustion Turbines source
category?
In its 2008 decision in Sierra Club v.
EPA, 551 F.3d 1019 (D.C. Cir. 2008), the
court vacated portions of two provisions
in the EPA’s CAA section 112 General
Provisions regulations governing the
emissions of HAP during periods of
SSM. Specifically, the court vacated the
SSM exemption contained in 40 CFR
63.6(f)(1) and 40 CFR 63.6(h)(1), holding
that under section 302(k) of the CAA,
emissions standards or limitations must
be continuous in nature and that the
SSM exemption violates the CAA’s
requirement that some CAA section 112
standards apply continuously.
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The EPA proposed to revise
provisions related to SSM that are not
consistent with the requirement that
standards apply at all times. More
information concerning our proposal on
SSM can be found in the proposed rule
(84 FR 15046). As discussed in the
proposal, the EPA proposed an
operational standard in lieu of a
numeric emission limit during periods
of startup, in accordance with CAA
section 112(h). The EPA proposed that
during turbine startup, owners and
operators must minimize the turbine’s
time spent at idle or holding at low load
levels and minimize the turbine’s
startup time to a period needed for
appropriate and safe loading of the
turbine, not to exceed 1 hour for simple
cycle stationary combustion turbines
and 3 hours for combined cycle
stationary combustion turbines, after
which time the formaldehyde emission
limitation of 91 ppbvd at 15-percent O2
would apply. We did not propose a
different standard that would apply
during shutdown.
2. How did the SSM provisions change
for the Stationary Combustion Turbines
source category?
In the final rule, we revised aspects of
the operational standard for startup
from the proposal based on public
comments. We removed the language
specifying that the owner or operator
must minimize the turbine’s time spent
at idle or holding at low levels and
minimize the turbine’s startup time to a
period needed for appropriate and safe
loading of the turbine. We have also
added a definition for startup that is
specific to stationary combustion
turbines, rather than using the general
definition in the General Provisions
(subpart A) of 40 CFR part 63. The
definition specifies that startup begins
at the first firing of fuel in the stationary
combustion turbine.
In response to comments regarding
the proposed operational standard for
startup and the proposed conclusion
that a standard for shutdown is not
necessary, the EPA evaluated Acid Rain
Program hourly emissions data for
stationary combustion turbines from
2018.6 The stabilization of NOx
emissions, an indicator of stable
combustion and post-combustion
processes, was used to determine
startup and shutdown times for turbines
subject to 40 CFR part 63, subpart
YYYY. Based on the Acid Rain Program
emissions data, the EPA determined that
6 See the memorandum titled Stationary
combustion turbine startups and shutdowns based
on Acid Rain Program CEMS data, which can be
found in the rulemaking docket (Docket ID No.
EPA–HQ–OAR–2017–0688).
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the majority of turbine startup times
were less than 1 hour for simple cycle
turbines and the majority of startup
times were less than 3 hours for
combined cycle turbines. Upper
prediction limits for the best performers
for startup time were also determined
following statistical methods used to
define upper prediction limits for
MACT emission standards (e.g.,
methods detailed in the memorandum,
CO CEMS MACT Floor Analysis August
2012 for the Industrial, Commercial,
and Institutional Boilers and Process
Heaters National Emission Standards
for Hazardous Air Pollutants Major
Source, Docket ID Item No. EPA–HQ–
OAR–2002–0058–3877). Upper
prediction limits were less than 1 hour
for simple cycle turbines and less than
3 hours for combined cycle turbines
regardless of startup type (i.e., cold,
warm, and hot starts). Additionally, the
majority of shutdown times were less
than 30 minutes for both simple cycle
and combined cycle turbines. Finally,
utilizing oxidation catalyst had minimal
effect on startup and shutdown times.
3. What key comments did we receive
on the SSM provisions, and what are
our responses?
Comment: Commenters stated that the
proposed rule does not define what
constitutes the period of startup,
including the beginning and the ending.
The commenters added that 40 CFR part
63 defines startup as ‘‘the setting in
operation of an affected source or
portion of an affected source for any
purpose.’’ The commenters stated that
this definition is vague and does not
specify when startup ends. The
commenters suggested that the EPA
provide a definition of startup as it
applies to simple cycle and combined
cycle combustion turbines. A
commenter also stated that some
combined cycle combustion turbines
can operate in simple cycle mode.
Therefore, the EPA also needs to
address these types of turbines in the
definitions or the standard itself,
according to the commenter. A
commenter added that the definition
used in the standard should not
interfere with the definition of startup
in other parts of the CAA or in operating
permits, nor should it constrain normal
operations. The commenter specifically
suggested that the EPA revise the
operational standard to apply only upon
the first firing of fuel in the combustion
turbine.
Response: The EPA agrees with the
commenters that it would be
appropriate to define startup as
beginning at the first firing of fuel in the
stationary combustion turbine and to
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specify when the startup standard ends.
The EPA has specified different startup
times for simple cycle and combined
cycle turbines, as discussed elsewhere
in this section. For simple cycle
turbines, the EPA has specified in the
final rule that startup ends when the
stationary combustion turbine has
reached stable operation or after 1 hour,
whichever is less. For combined cycle
turbines, startup ends when the
stationary combustion turbine has
reached stable operation or after 3
hours, whichever is less. If a turbine in
a combined cycle configuration is
operating as a simple cycle turbine, it
must follow the requirements for simple
cycle turbines. Regarding the comment
that the definition should not interfere
with the definition of startup in other
parts of the CAA or in operating permits
or constrain normal operations, the EPA
does not anticipate any interference. As
discussed elsewhere in this section, the
standard is based on turbine startup
times gathered from emissions data, and
it also allows the turbine to take longer
to start up if needed (while requiring
that the turbine meet the applicable
formaldehyde limit).
Comment: Many commenters
expressed support for the establishment
of the operational standard during
startup operations but asserted that the
EPA must allow more time for certain
startup operations for combined cycle
stationary combustion turbines. Some
commenters stated that they believe the
record does not demonstrate the
feasibility of a 3-hour startup time for
combined cycle units. They added that
it appears the 3-hour limit was taken
from a document from the Gas Turbine
Association (Docket ID Item No. EPA–
HQ–OAR–2017–0688–0033). These
commenters stated that while this
document discusses a period of 3 hours
for startup, the document also discusses
the wide range of variability in the time
needed. Several commenters explained
that the startup time for a combined
cycle turbine is impacted by its
integration with other site facilities and
the type of startup. Some commenters
cited specific instances when additional
startup time beyond what was proposed
for combined cycle turbines may be
expected, including:
• Startups following extended
downtime or a unit turnaround which
commenters asserted may take up to 10
hours. A commenter provided a list of
nine major steps for startup following a
unit turnaround in their comment letter
to support the need for additional
startup time;
• startup involving combined heat
and power units as the startup typically
involves purging and setup of the heat
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recovery steam generator, followed by
gas speed-up and loading, followed by
the steam turbine speedup and loading;
• various types of startup including a
‘‘warm’’ start (i.e., when the steam
turbine first stage or reheat inner metal
temperature is between 400 and 700
degrees Fahrenheit) and a ‘‘cold’’ start
(i.e., when the steam turbine first stage
or reheat inner metal temperature is less
than 400 degrees Fahrenheit). One
commenter reviewed operating data
from 2017–2019 for some of its
stationary combined cycle combustion
turbines, noting that 32 out of 82
‘‘warm’’ startups exceeded a 3-hour
duration with an average duration of
3.3–4 hours, and all 23 of the ‘‘cold’’
startups exceeded the 3-hour duration
with an average duration of 5–6 hours.
Another commenter stated that member
companies will be submitting facilityspecific data showing the impact of
startup type on duration;
• startup involving gas fuel turbines
integrated with other systems associated
with multiple boilers to produce
electricity and steam for a large
manufacturing complex; and
• pre-startup commissioning
activities and initial startup at liquid
natural gas terminals.
These commenters suggested that the
EPA provide additional time in the
startup operational standard for
combined cycle turbines.
Some commenters suggested that 4
hours be provided in the standard.
Other commenters suggested that the
EPA allow 5.5 hours as the baseline
with provisions for site-specific requests
for additional time. Some commenters
suggested that the final action should
provide a procedure for the EPA or state
permitting authorities to provide
application of an alternative standard
for combined cycle turbines if an
operator demonstrates that it is needed.
A commenter suggested that the EPA
allow between 6–8 hours in the
standard. Another commenter suggested
that the EPA allow up to 10 hours in the
standard. One commenter suggested
that, consistent with their state
operating permit requirements and due
to the unique nature of their operations,
the EPA should allow up to 12 hours in
the standard. Another commenter added
that the EPA could provide different
time frames if they differentiated
between different startup types (i.e.,
provide the most time for cold startups
and the least time for hot startups).
Alternatively, other commenters
suggested that the EPA could maintain
the 3-hour standard for combined cycle
turbines but allow a more extended
startup time to facilities if they
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document the need for the additional
startup time; maintain associated
records; provide semi-annual reporting;
and take steps during the startup to
minimize emissions consistent with
good air pollution control practices.
Commenters suggested the standard
should require that owners and
operators of combined cycle units
minimize the time the turbines spend at
idle or low load operations, and that
they complete the startup process while
operating the equipment in a manner
consistent with good air pollution
control practices for minimizing
emissions, rather than having the EPA
impose a one-size-fits-all hour limit.
One commenter suggested that the end
of the startup period should be when
the unit begins to operate in ‘‘normal
mode’’ as signaled from the turbine
control system. Commenters also
suggested that if the EPA maintains an
hour limit, the standard should be
amended to exclude malfunctions
encountered during startup from the
calculation of the startup time as such
events could cause sources to exceed
the window.
One commenter recommended that
the final rule not supersede site-specific
requirements with a one-size-fits-all
approach. The commenter suggested
that the final standard include approved
procedural work practices to provide
additional assurance of an efficient and
expeditious startup process (i.e., a
procedural startup work practice could
specify that ammonia injection would
begin when the catalyst temperature
meets a certain minimum temperature).
According to the commenter, these
procedural work practices can be
maintained, submitted, and approved by
the administrator outside of the air
permit to minimize permit changes
similar to the way quality assurance/
quality control manuals are handled.
One commenter suggested that if a
more generic startup requirement
cannot not be implemented, the EPA
should address any imposition of a time
limit for startup of a reconstructed
combined cycle unit on a case-by-case
basis in recognition of the diverse
combined cycle plant designs and how
such designs impact the rate at which
startup can be achieved.
As with the proposed operational
standard for combined cycle turbines,
several commenters expressed support
for the proposed operational standard
for simple cycle turbines during startup
but expressed concern with the amount
of time provided for startup.
Commenters noted that 1 hour for a
simple cycle turbine is sufficient in
most cases, however, the commenter
explained that the EPA should provide
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additional time for extenuating
circumstances including the startup of
associated post-combustion control
technology which can take over an hour
to warm-up and achieve the required
destruction rate. One commenter added
that initial commissioning or
maintenance may require additional
startup time. The commenter suggested
that the EPA allow longer startup times
and require facilities utilizing a longer
startup time to document the
circumstance in their periodic report to
ensure there was a reasonable basis.
Similarly, other commenters stated
that more time should be provided for
simple cycle turbines and suggested that
the EPA provide 2 hours consistent with
some state permits. One commenter
asserted that the federal requirements
should not contradict state operating
permit conditions already in place
which provide more time than the
proposed rule. Commenters stated that
the final action should provide a
procedure for the EPA or state
permitting authority to provide
application of an alternative standard if
an operator demonstrates that it is
needed.
Response: In the final action, the
definition of startup is specified to begin
at the initial combustion of fuel in the
turbine. Other operations prior to this
event are not included in the time
period allocated for startup in this rule.
In response to the comments that the
proposed time limit for startup in the
operational standard for startup was not
sufficient, as discussed previously in
this section, the EPA reviewed
continuous emission monitoring
systems (CEMS) data from 2018 for 182
turbines subject to 40 CFR part 63,
subpart YYYY. This includes both
simple and combined cycle turbines
representing a range of different designs.
The analysis is documented in the
memorandum titled Stationary
Combustion Turbine Startups and
Shutdowns Based on Acid Rain Program
CEMS Data, which can be found in the
rulemaking docket (Docket ID No. EPA–
HQ–OAR–2017–0688). As discussed in
the memorandum, the stabilization of
NOX emission rates indicates stable
operation (i.e., of combustion and postcombustion controls) and was used to
determine the length of startup and
shutdown periods. For simple cycle
turbines, 90 percent of startups were
less than 1 hour for stabilization of
emissions for all startup types (i.e.,
‘‘cold,’’ ‘‘warm,’’ ‘‘hot’’; turbine out of
operation for more than 48 hours, 8–48
hours, and 0–8 hours, respectively). For
combined cycle turbines, 90 percent of
‘‘warm’’ and ‘‘hot’’ startups were less
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than 3 hours and 72 percent of ‘‘cold’’
startups were less than 3 hours.
In a second part of the analysis, the
EPA reviewed CEMS data from 2018 for
turbines with oxidation catalyst. For
simple cycle turbines with oxidation
catalyst, 80 percent of cold startups, 76
percent of warm startups, and 93
percent of hot startups were less than 1
hour. For combined cycle turbines with
oxidation catalyst, at least 93 percent of
startups were less than 3 hours for each
startup type. Finally, in all cases the 99percent upper prediction limits for
startup of turbines were within the
proposed time limits (at most 0.92 hours
for cold starts for simple cycle turbines
with oxidation catalyst and 2.93 hours
for cold starts for combined cycle
turbines subject to 40 CFR part 63,
subpart YYYY). Upper prediction limits
were determined for the best performing
turbines in terms of startup time based
on NOX emission stabilization.
As noted in the memorandum, NOX
emissions were not used as a surrogate
for HAP emissions. Rather, NOX
emissions were only used as an
indicator for when stabilization of
combustion and post-combustion
processes may occur. Collectively, the
analyses demonstrate that time limits in
the proposed operational standards for
startup are justified. Furthermore, upper
prediction limits for the startup time to
stabilization of NOX emissions were
near the startup time limits of 1 hour for
simple cycle turbines and 3 hours for
combined cycle turbines, suggesting that
the startup time limits are generally
neither too short nor too long with
respect to emissions stabilization.
Based on the review of CEMS data,
the EPA determined that the proposed
time limits for the application of the
operational standard for startup are
reasonable and consistent with what the
best performers achieve. Therefore, the
EPA is not changing the proposed time
limits based on public comments.
Regarding the comments that the EPA
should address time limits on a case-bycase basis, if situations occur that
warrant an alternative standard, the
owner/operator can request an
alternative standard pursuant to the
requirements specified in CAA section
112(h)(3) and 40 CFR 63.6(g).
Comment: Commenters stated that the
requirement within the proposed
operational standard to ‘‘minimize the
turbine’s time spent at idle or holding
at low load levels’’ is problematic in
their opinion.
One commenter stated that greater
clarity is needed between what is
termed ‘‘startup’’ and what is termed
‘‘idle’’ in the process. The commenter
explained that startup by its very nature
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begins at ‘‘low load levels’’ before the
turbine is safely loaded and questioned
where is the dividing line between
which levels are considered startup and
which levels are considered idle, or,
alternatively, at what point in time do
low load levels of startup become idle
low load levels? The commenter stated
that implicit in the proposed distinction
seems to be the assumption that
operators would run a turbine at ‘‘idle’’
for unknown reasons during the startup
process. The commenter asserted that
this is contrary to generally accepted
operating practices. See, e.g., Sierra
Club v. EPA, 884 F.3d 1185, 1203 (D.C.
Cir. 2018) (‘‘Boiler operators lack
incentives to combust fuel for no useful
purpose, simply as a means to avoid
engaging pollution controls, so
presumably they do not tarry in heating
their equipment to that point.’’).
One commenter stated that the terms
‘‘idle’’ and ‘‘holding at low load levels’’
have not been defined. The commenter
asserted that without defining these
terms and how the EPA intends for
units to measure compliance with the
operational standard, it is unclear what
standards combustion turbine operators
need to meet outside of their existing
permit terms. The commenter stated
that the proposed language in Table 1 to
40 CFR part 63, subpart YYYY,
therefore, creates confusion as to
whether these combustion turbines can
continue to operate as intended. Other
commenters explained that combustion
turbines are often designed, built,
permitted, and operated to be loadfollowing and to sometimes idle or be
held at low load, when necessary, to
enable faster ramping as support for
intermittent renewable resources (e.g.,
solar panels). A commenter stated that
some operators may need to hold a
combustion turbine at low load to allow
the heat recovery steam generator and
steam turbine associated with a
combined cycle to reach normal
operating temperature. According to the
commenter, the metal in the steam
turbine must be warmed in a controlled
manner to allow the proper expansion
of moving parts. The commenter stated
that once the heat recovery steam
generator and steam turbine metal are
properly warmed and expanded, the
combined cycle can, at that time, ramp
up load to meet demand. The
commenter contended that any artificial
restrictions on the amount of minimum
operating time allowed may require
turbine operators to risk damaging
critical equipment. The commenter
added that good engineering practices
require testing at low loads following a
planned maintenance outage to ensure
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the equipment is operating safely and
performing as expected. The commenter
stated that some manufacturers require
this type of testing as part of contractual
agreement. Therefore, the commenter
suggested that the operational standard
be revised as follows: ‘‘During turbine
startup, you must minimize the
turbine’s time needed to achieve the
operating limitations provided in Table
2, taking into account the appropriate
and safe loading of the turbine and
auxiliary equipment, not to exceed 1
hour for simple cycle stationary
combustion turbines and 3 hours for
combined cycle stationary combustion
turbines, after which time the operating
limitation and continuous compliance
requirements in Table 2 and 5 apply.’’
Another commenter provided an
example of a Prevention of Significant
Deterioration permit that has
specifically authorized operation at low
loads in order to provide fast-ramping
capacity to support the integration of
renewable resources (e.g., Maricopa
County Air Quality Permit Department,
Title V Permit No. V95–007, ‘‘Ocotillo
PSD Permit’’). The commenter noted
that the permit conditions clearly
distinguish between ‘‘startup’’ and
operation at low load. The commenter
also noted that the EPA’s Environmental
Appeals Board reviewed and approved
the Prevention of Significant
Deterioration limits in this permit.
One commenter suggested that the
EPA amend the proposed language to
allow adequate time to ensure safe
loading of the turbine even if it is
beyond the otherwise applicable startup
time limits.
Another commenter stated that, at a
minimum, the standard should not be
written to prohibit low loads, especially
if the unit is equipped with an oxidation
catalyst and can meet its 4-hour average
catalyst inlet temperature operating
limit during low load operation.
One commenter recommended that
the EPA either eliminate the proposed
requirement, ‘‘minimize the turbine’s
time spent at idle or holding at low load
levels’’ or clarify the proposed language
by replacing the phrase ‘‘time spent at
idle or holding at low load levels’’ with
the phrase ‘‘operating time outside
normal operations.’’
Other commenters concluded that the
EPA should not finalize this
requirement as part of the operational
standard.
One commenter encouraged the EPA
to revise the operational standard for
startup in a manner that distinguishes
between continuous, stable operation at
low loads and true startup conditions.
Response: Based on these comments,
the EPA is not finalizing the proposed
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requirement to minimize a turbine’s
time spent at idle or holding at low load
levels. As stated by the commenters,
some turbines are designed and
permitted to operate at idle or low load
conditions. For the final rule, there will
not be an operational requirement to
minimize time spent operating in an
idle or low load status. Operation in
such a status (except during startup)
will be treated as normal operation and
will not have a separate standard. As
discussed elsewhere in this section, the
EPA has clarified the definition for
startup to distinguish the beginning and
end of the startup operational standard.
Comment: One commenter noted that
40 CFR 63.6125 states, ‘‘If you are
operating a stationary combustion
turbine that is required to comply with
the formaldehyde emission limitation
and you use an oxidation catalyst
emission control device, you must
monitor on a continuous basis your
catalyst inlet temperature in order to
comply with the operating limitation in
Table 2 and as specified in Table 5 of
this subpart.’’ The commenter then
pointed out that Tables 2 and 5 refer to
the calculation of a 4-hour rolling
average catalyst inlet temperature. The
commenter explained that the catalyst
must achieve a certain inlet temperature
before formaldehyde emissions are
controlled, so the inlet temperature
monitoring should begin at the
conclusion of startup. The commenter
suggested that the EPA clarify that the
calculation of the 4-hour rolling average
begins at the start of the first full clock
hour after startup.
For the same reasons (i.e., turbines
using an oxidation catalyst will need
time to reach the desired temperature),
other commenters suggested that the
EPA clarify that the operating
limitations in Table 2 do not apply
during startup. These commenters also
suggested that the operating limits in
Table 2 not apply during shutdown as
the inlet temperature may fall below the
desired level as the combustion turbine
transitions out of operation.
One commenter also requested that
the EPA clarify that the demonstration
of continuous compliance with the
operating limits specified in Table 5 do
not include hours containing SSM in
the calculation. The commenter
recommended that the EPA revise the
operating limitations in Table 5 of 40
CFR part 63, subpart YYYY to include
the following language, ‘‘Any hour
during which the startup work practice
standard is applicable or during which
shutdown or malfunction occurs must
not be included in the calculation to
demonstrate continuous compliance
with the operating limitation.’’
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Response: The EPA agrees with the
commenter that the catalyst inlet
temperature operating limitation should
not apply during startup, since the
catalyst needs time to heat up to the
required temperature. The EPA has
revised the rule to reflect this change.
The EPA does not agree that the catalyst
inlet temperature recorded during
periods of shutdown should not be
included in the 4-hour rolling average
catalyst inlet temperature used for
compliance with the catalyst inlet
temperature operating limitation. Our
information is that shutdown periods
are usually brief and there is no
information that the catalyst
temperature would fall below the
required levels while the turbine is still
operating. Since compliance with the
operating limitation is demonstrated on
a 4-hour rolling average, factoring in
brief periods of shutdown should not
result in exceedances of the operating
limitation.
With respect to malfunctions, the EPA
is not establishing separate emission
standards for periods of malfunction
and the formaldehyde emission
standards and the associated catalyst
inlet temperature monitoring
requirements apply during periods of
malfunction. Therefore, we did not
accept the commenter’s
recommendation that the catalyst inlet
temperature during a malfunction
should be excluded from the calculation
of the 4-hour rolling average catalyst
inlet temperature. The EPA also notes
that catalyst inlet temperatures may not
be affected by all types of malfunction.
In addition, as discussed in the
proposed rule, if a source fails to
comply with a requirement as a result
of a malfunction event, the EPA would
determine an appropriate response and
if the EPA determines in a particular
case that an enforcement action against
a source for violation of an emission
standard is warranted, the source can
raise any and all defenses in that
enforcement action. Administrative and
judicial procedures for addressing
exceedances of the standards fully
recognize that violations may occur
despite good faith efforts to comply and
can accommodate those situations. U.S.
Sugar Corp. v. EPA, 830 F.3d 579, 606–
610 (2016).
4. What is the rationale for our final
approach for the SSM provisions?
For the reasons explained in the
proposed rule (84 FR 15046), these
amendments revise provisions related to
SSM that are not consistent with the
requirement that the standards must
apply at all times. We evaluated all of
the comments received on the EPA’s
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proposed amendments to the SSM
provisions and made some changes to
the proposed amendments for the
reasons stated above and in the
Summary of Public Comments and
Responses document. We are finalizing
the proposed amendments to revise
provisions related to SSM, as revised
based on public comments.
D. Electronic Reporting Requirements
for the Stationary Combustion Turbines
Source Category
1. What did we propose for the
Stationary Combustion Turbines source
category?
The April 12, 2019, proposal included
requirements for owners and operators
of stationary combustion turbines
subject to 40 CFR part 63, subpart YYYY
to submit electronic copies of required
performance test results and semiannual
compliance reports through the EPA’s
CDX using CEDRI. The original 2004
rule did not include any requirements
for electronic reporting.
2. How did the electronic reporting
requirements change for the Stationary
Combustion Turbines source category?
The proposed amendments to require
owners and operators to submit
performance test results and semiannual
compliance reports through the EPA’s
CDX using CEDRI are being finalized
with minor corrections and
clarifications. The language at 40 CFR
63.6150(a) was amended from the
proposal to specify that the electronic
report submitted semiannually also
incorporates the excess emissions and
monitoring system performance reports.
The delegation of authority provision at
40 CFR 63.6170(c) was amended to
specify that the EPA does not delegate
the authority to modify electronic
reporting requirements to states, to
ensure that the reported information is
submitted to the EPA. Table 7 of 40 CFR
part 63, subpart YYYY was modified to
make inapplicable the requirements in
40 CFR 63.13 for submission of
additional copies to the EPA Regional
office for electronically submitted
reports.
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3. What key comments did we receive
on the electronic reporting
requirements, and what are our
responses?
Comment: Commenters stated that the
electronic reporting provisions should
clarify the electronic reporting
requirements as they relate to reports
submitted to state agencies and should
consider the increase in burden if
owners/operators must submit reports to
both entities rather than submitting one
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combined report to their delegated
authority.
One commenter stated that as
proposed, the owner/operator would be
required to submit one report to the EPA
through the CEDRI system and then be
required to prepare a written report for
state agencies such as the Texas
Commission on Environmental Quality
to satisfy the regulatory reporting
obligation, thus creating a redundant
reporting requirement. The commenter
requested that the final rule clarify
whether the electronic reporting
requirement also applies to affected
sources that are not currently required
to submit copies of reports to the EPA
because they are located in states like
Texas that have received delegation for
NESHAP under 40 CFR part 63.
One commenter stated that when
developing electronic reporting
provisions, the EPA should work with
other regulatory authorities (i.e., states,
local agencies) to establish comparable
or compatible electronic systems. The
commenter noted that companies
reporting electronically to the EPA will
likely still have to submit hardcopy
reports to other agencies that do not
have electronic systems, thereby
reducing or eliminating any burden
savings associated with EPA electronic
reporting. In one example, based on the
template structure, an annual number
for landfill gas fuel rate and heating
values would be supplied to the EPA
but monthly values would still have to
be supplied to the state.
One commenter stated that if the EPA
finalizes a requirement for submission
of electronic reports to CEDRI, the EPA
should make inapplicable the
requirement in 40 CFR 63.13 for
submission of additional copies to the
EPA Regional office. According to the
commenter, submission to CEDRI
should be deemed compliance with that
requirement, because EPA Regional
employees can access the reports on
CEDRI. The commenter recommended
that the EPA also should include a
procedure for state agencies to similarly
opt out of receiving a paper copy.
Similarly, one commenter noted that
the EPA did not add an additional
burden related to the requirement to
report emissions test data using the ERT
within the Supporting Statement for the
Information Collection Request. The
commenter stated that most state or
local permitting authorities will still
require submittal of a paper copy of the
test report, so the ERT entry and
electronic submittal to the EPA does not
replace the submittal of a test report to
the local agency.
Response: To clarify the EPA’s intent
that electronic reporting is required for
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all sources subject to the subpart,
regardless of state, local, or tribal
reporting requirements, the final rule
has been amended at 63.6170(c) to add
(6), that the EPA does not delegate
authority for electronic reporting
requirements. The EPA is not delegating
the authority in order to ensure that the
information required to be reported is
received by the EPA. The reported
information is needed for several
purposes, including assessing
compliance, developing emission
factors (in the case of emissions data),
and future reviews of the NESHAP.
Table 7 has been revised for the final
rule to reflect that 63.13(a) is only
applicable to those reports not required
to be submitted electronically.
We acknowledge that certain sources
may be required to submit a report
electronically through CEDRI and a hard
copy report to an air agency that has
delegation to enforce the NESHAP. The
ERT is designed to provide PDF or
printed copies of reports, and these
copies can be mailed to an air agency
that does not wish to use the EPA’s
electronic reporting system. The burden
associated with creating an emission
test report is incorporated in the cost of
the emission test presented in the
Supporting Statement for the
Information Collection Request (Docket
ID Item No. EPA–HQ–OAR–2017–0688–
0073). This includes the development of
the test report through the ERT.
The EPA routinely discusses
electronic reporting with air agencies
and EPA Regional offices. Quarterly
calls are conducted with EPA Regional
offices to provide information that will
be helpful in their outreach efforts to the
air agencies in their regions. The EPA
has performed demonstrations of the
CEDRI reporting program and the ERT
for EPA Regional offices and their
associated air agencies, as well as for air
agency groups like the Mid-Atlantic
Regional Air Management Association.
Additionally, through the EEnterprise’s Combined Air Emissions
Reporting (CAER) project, the EPA is
working with air agencies to streamline
multiple emissions reporting processes.
Currently, air emissions information is
collected by the EPA and air agencies
through numerous separate regulations,
in a variety of formats, according to
different reporting schedules, and using
multiple routes of data transfer. The
CAER project seeks to reduce the cost to
industry and government for providing
and managing important environmental
data. More information on CAER can be
found at: https://www.epa.gov/eenterprise/e-enterprise-combined-airemissions-reporting-caer.
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4. What is the rationale for our final
approach for the electronic reporting
requirements?
The EPA evaluated all of the
comments on the proposed electronic
reporting requirements for this subpart.
For the reasons explained in the
proposed rule and this final rule,
including the document in the docket
summarizing the public comments and
our responses,7 we are finalizing the
amendments with minor changes.
V. Summary of Cost, Environmental,
and Economic Impacts and Additional
Analyses Conducted
A. What are the affected facilities?
The EPA has identified 777 turbines
at 243 facilities that are currently
subject to the Stationary Combustion
Turbines NESHAP. We are projecting
that 51 new stationary combustion
turbines at 20 facilities will become
subject to the NESHAP over the next 3
years. The 51 new turbines include 48
natural gas-fired units, one oil-fired
unit, and two landfill gas or digester
gas-fired units. More information about
the number of new turbines projected
over the next 3 years can be found in the
Projected Number of Turbine Units and
Facilities Subject to the Stationary
Combustion Turbine National Emission
Standards for Hazardous Air (NESHAP)
memorandum in the docket for this
rulemaking (Docket ID No. EPA–HQ–
OAR–2017–0688).
B. What are the air quality impacts?
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The baseline emissions of HAP for
777 stationary combustion turbines at
243 facilities subject to 40 CFR part 63,
subpart YYYY are estimated to be 5,466
tpy. The HAP that is emitted in the
largest quantity is formaldehyde. The
final amendments will require turbines
subject to the Stationary Combustion
Turbines NESHAP to operate without
the SSM exemption. We were unable to
quantify emission reductions associated
with eliminating the SSM exemption.
However, eliminating the SSM
exemption will reduce emissions by
requiring facilities to meet the
applicable standard during periods of
SSM. We are not making any other
revisions to the emission limits, so there
are no other air quality impacts as a
result of the final amendments.
7 National Emission Standards for Hazardous Air
Pollutants from Stationary Combustion Turbines
(40 CFR part 63, subpart YYYY) Residual Risk and
Technology Review, Final Amendments, Summary
of Public Comments and Responses on Proposed
Rule, January 2020.
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C. What are the cost impacts?
Owners or operators of stationary
combustion turbines that are subject to
the amendments to 40 CFR part 63,
subpart YYYY, will incur costs to
review the final rule. Nationwide
annual costs associated with reviewing
the final rule are estimated to be a total
of $42,362 (2017 dollars) for the first
year after the final rule only, or
approximately $174 (2017 dollars) per
facility. We do not expect that the
amendments revising the SSM
provisions and requiring electronic
reporting will impose additional burden
and may result in a cost savings.
D. What are the economic impacts?
Economic impact analyses focus on
changes in market prices and output
levels. If changes in market prices and
output levels in the primary markets are
significant enough, impacts on other
markets may also be examined. Both the
magnitude of costs needed to comply
with a proposed rule and the
distribution of these costs among
affected facilities can have a role in
determining how the market will change
in response to a proposed rule. The total
costs associated with reviewing the final
rule are estimated to be $42,362 (2017
dollars), or $174 (2017 dollars) per
facility, for the first year after the final
rule. These costs are not expected to
result in a significant market impact,
regardless of whether they are passed on
to the purchaser or absorbed by the
firms.
13537
within the populations living near
facilities. The results of this analysis
indicated that this action does not have
disproportionately high and adverse
human health or environmental effects
on minority populations, low-income
populations, and/or indigenous peoples.
The documentation for this decision is
contained in section IV.A of the
preamble to the proposed rule and the
technical report titled Risk and
Technology Review—Analysis of
Demographic Factors for Populations
Living Near Stationary Combustion
Turbines Source Category Operations,
which is available in the docket for this
action (Docket ID No. EPA–HQ–OAR–
2017–0688).
G. What analysis of children’s
environmental health did we conduct?
This action’s health and risk
assessments are contained in sections
IV.A and B of this preamble and further
documented in the risk report titled
Residual Risk Assessment for the
Stationary Combustion Turbines Source
Category in Support of the 2020 Risk
and Technology Review Final Rule,
which is available in the docket for this
action (Docket ID No. EPA–HQ–OAR–
2017–0688).
VI. Statutory and Executive Order
Reviews
Additional information about these
statutes and Executive Orders can be
found at https://www.epa.gov/lawsregulations/laws-and-executive-orders.
E. What are the benefits?
The EPA is not making changes to the
emission limits and estimates that the
changes to the SSM requirements and
requirements for electronic reporting are
not economically significant. Because
these amendments are not considered
economically significant, as defined by
Executive Order 12866, and because no
emission reductions were projected, we
did not estimate any benefits from
reducing emissions.
A. Executive Orders 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
F. What analysis of environmental
justice did we conduct?
As discussed in the preamble to the
proposed rule, to examine the potential
for any environmental justice issues that
might be associated with the source
category, we performed a demographic
analysis, which is an assessment of risks
to individual demographic groups of the
populations living within 5 kilometers
(km) and within 50 km of the facilities.
In the analysis, we evaluated the
distribution of HAP-related cancer and
noncancer risks from the Stationary
Combustion Turbines source category
across different demographic groups
This action is not an Executive Order
13771 regulatory action because this
action is not significant under Executive
Order 12866.
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This action is not a significant
regulatory action and was, therefore, not
submitted to the Office of Management
and Budget (OMB) for review.
B. Executive Order 13771: Reducing
Regulations and Controlling Regulatory
Costs
C. Paperwork Reduction Act (PRA)
This action does not impose any new
information collection burden under the
PRA. OMB has previously approved the
information collection activities
contained in the existing regulations
and has assigned OMB control number
2060–0540. We do not expect that the
final amendments revising the SSM
provisions and requiring electronic
reporting will impose additional burden
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not already accounted for under the
existing approved burden.
D. Regulatory Flexibility Act (RFA)
I certify that this action will not have
a significant economic impact on a
substantial number of small entities
under the RFA. The small entities
subject to the requirements of this
action are small energy companies or
governmental jurisdictions. The Agency
has determined that 10 small entities
representing approximately 4 percent of
the total number of entities subject to
the final rule may experience an impact
of less than 0.1 percent of revenues.
E. Unfunded Mandates Reform Act
(UMRA)
This action does not contain an
unfunded mandate of $100 million or
more as described in UMRA, 2 U.S.C.
1531–1538, and does not significantly or
uniquely affect small governments. The
action imposes no enforceable duty on
any state, local, or tribal governments or
the private sector.
F. Executive Order 13132: Federalism
This action does not have federalism
implications. It will not have substantial
direct effects on the states, on the
relationship between the national
government and the states, or on the
distribution of power and
responsibilities among the various
levels of government.
G. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This action does not have tribal
implications as specified in Executive
Order 13175. None of the stationary
combustion turbines that have been
identified as being affected by this
action are owned or operated by tribal
governments or located within tribal
lands. Thus, Executive Order 13175
does not apply to this action.
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H. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
This action is not subject to Executive
Order 13045 because it is not
economically significant as defined in
Executive Order 12866, and because the
EPA does not believe the environmental
health or safety risks addressed by this
action present a disproportionate risk to
children. This action’s health and risk
assessments are contained in sections
III.A and B and sections IV.A and B of
this preamble, and further documented
in the risk document.
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I. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not subject to Executive
Order 13211, because it is not a
significant regulatory action under
Executive Order 12866.
J. National Technology Transfer and
Advancement Act (NTTAA) and 1 CFR
Part 51
This action involves technical
standards. The EPA has decided to use
ANSI/ASME PTC 19.10–1981 Part 10
(1981), ‘‘Flue and Exhaust Gas
Analyses’’ (the manual portion only) as
an alternative to EPA Method 3B and to
incorporate the alternative method by
reference. The ANSI/ASME PTC 19.10–
1981 Part 10 (1981) method incorporates
both manual and instrumental
methodologies for the determination of
O2 content. The manual method
segment of the O2 determination is
performed through the absorption of O2.
The method is reasonably available from
the American Society of Mechanical
Engineers at https://www.asme.org; by
mail at Three Park Avenue, New York,
NY 10016–5990; or by telephone at
(800) 843–2763. The EPA has decided to
use ASTM D6522–11, ‘‘Standard Test
Method for the Determination of
Nitrogen Oxides, Carbon Monoxide, and
Oxygen Concentrations in Emissions
from Natural Gas-Fired Reciprocating
Engines, Combustion Turbines, Boilers
and Process Heaters Using Portable
Analyzers’’ as an alternative to EPA
Method 3A for turbines fueled by
natural gas and to incorporate the
alternative method by reference. The
ASTM D6522–11 method is an
electrochemical cell based portable
analyzer method which may be used for
the determination of NOX, CO, and O2
in emission streams form stationary
sources. Also, instead of the current
ASTM D6348–12e1 standard
(‘‘Determination of Gaseous Compounds
by Extractive Direct Interface Fourier
Transform Infrared (FTIR)
Spectroscopy’’), the Stationary
Combustion Turbines NESHAP
currently references ASTM D6348–03 as
an alternative to EPA Method 320. We
are updating the NESHAP to reference
the most current version of the ASTM
D6348 method as an alternative to EPA
Method 320. When using this method,
the test plan preparation and
implementation requirements in
Annexes A1 through A8 to ASTM
D6348–12e1 are mandatory. The ASTM
D6348–12e1 method is an extractive
FTIR spectroscopy-based field test
method and is used to quantify gas
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phase concentrations of multiple target
compounds in emission streams from
stationary sources. The ASTM standards
are reasonably available from the
American Society for Testing and
Materials, 100 Barr Harbor Drive, Post
Office Box C700, West Conshohocken,
PA 19428–2959. See https://
www.astm.org/.
The EPA identified an additional
seven voluntary consensus standards
(VCS) as being potentially applicable to
this rule. After reviewing the available
standards, the EPA determined that the
seven VCS would not be practical due
to lack of equivalency, documentation,
validation data, and/or other important
technical and policy considerations. For
further information, see the
memorandum titled Voluntary
Consensus Standard Results for
National Emission Standards for
Hazardous Air Pollutants: Stationary
Combustion Turbines Risk and
Technology, in the docket for this rule
(Docket ID No. EPA–HQ–OAR–2017–
0688).
K. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
The EPA believes that this action does
not have disproportionately high and
adverse human health or environmental
effects on minority populations, lowincome populations, and/or indigenous
peoples, as specified in Executive Order
12898 (59 FR 7629, February 16, 1994).
The documentation for this decision
is contained in section IV.A of this
preamble and the technical report, Risk
and Technology Review Analysis of
Demographic Factors for Populations
Living Near Stationary Combustion
Turbines Source Category Operations.
L. Congressional Review Act (CRA)
This action is subject to the CRA, and
the EPA will submit a rule report to
each House of the Congress and to the
Comptroller General of the United
States. This action is not a ‘‘major rule’’
as defined by 5 U.S.C. 804(2).
List of Subjects in 40 CFR Part 63
Environmental protection,
Administrative practice and procedures,
Air pollution control, Hazardous
substances, Incorporation by reference,
Intergovernmental relations, Reporting
and recordkeeping requirements.
Dated: January 31, 2020.
Andrew R. Wheeler,
Administrator.
For the reasons set forth in the
preamble, the EPA amends 40 CFR part
63 as follows:
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§ 63.6105 What are my general
requirements for complying with this
subpart?
PART 63—NATIONAL EMISSION
STANDARDS FOR HAZARDOUS AIR
POLLUTANTS FOR SOURCE
CATEGORIES
1. The authority citation for part 63
continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
Subpart A—General Provisions
2. Section 63.14 is amended by
revising paragraphs (e)(1) and (h)(85),
redesignating paragraphs (h)(94)
through (111) as (h)(95) through (112),
and adding new paragraph (h)(94) to
read as follows.
■
§ 63.14
Incorporations by reference.
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*
*
*
*
*
(e) * * *
(1) ANSI/ASME PTC 19.10–1981,
Flue and Exhaust Gas Analyses [Part 10,
Instruments and Apparatus], issued
August 31, 1981, IBR approved for
§§ 63.309(k), 63.457(k), 63.772(e) and
(h), 63.865(b), 63.1282(d) and (g),
63.1625(b), 63.3166(a), 63.3360(e),
63.3545(a), 63.3555(a), 63.4166(a),
63.4362(a), 63.4766(a), 63.4965(a),
63.5160(d), table 4 to subpart UUUU,
table 3 to subpart YYYY, 63.9307(c),
63.9323(a), 63.11148(e), 63.11155(e),
63.11162(f), 63.11163(g), 63.11410(j),
63.11551(a), 63.11646(a), and 63.11945,
table 5 to subpart DDDDD, table 4 to
subpart JJJJJ, table 4 to subpart KKKKK,
tables 4 and 5 to subpart UUUUU, table
1 to subpart ZZZZZ, and table 4 to
subpart JJJJJJ.
*
*
*
*
*
(h) * * *
(85) ASTM D6348–12e1, Standard
Test Method for Determination of
Gaseous Compounds by Extractive
Direct Interface Fourier Transform
Infrared (FTIR) Spectroscopy, Approved
February 1, 2012, IBR approved for
§ 63.1571(a) and table 3 to subpart
YYYY.
*
*
*
*
*
(94) ASTM D6522–11, Standard Test
Method for Determination of Nitrogen
Oxides, Carbon Monoxide, and Oxygen
Concentrations in Emissions from
Natural Gas-Fired Reciprocating
Engines, Combustion Turbines, Boilers,
and Process Heaters Using Portable
Analyzers, Approved December 1, 2011,
IBR approved for table 3 to subpart
YYYY.
*
*
*
*
*
Subpart YYYY—National Emission
Standards for Hazardous Air Pollutants
for Stationary Combustion Turbines
■
3. Revise § 63.6105 to read as follows:
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(a) Before September 8, 2020, you
must be in compliance with the
emission limitations and operating
limitations which apply to you at all
times except during startup, shutdown,
and malfunctions. After September 8,
2020, you must be in compliance with
the emission limitations, operating
limitations, and other requirements in
this subpart which apply to you at all
times.
(b) Before September 8, 2020, if you
must comply with emission and
operating limitations, you must operate
and maintain your stationary
combustion turbine, oxidation catalyst
emission control device or other air
pollution control equipment, and
monitoring equipment in a manner
consistent with good air pollution
control practices for minimizing
emissions at all times including during
startup, shutdown, and malfunction.
(c) After September 8, 2020, at all
times, the owner or operator must
operate and maintain any affected
source, including associated air
pollution control equipment and
monitoring equipment, in a manner
consistent with safety and good air
pollution control practices for
minimizing emissions. The general duty
to minimize emissions does not require
the owner or operator to make any
further efforts to reduce emissions if
levels required by the applicable
standard have been achieved.
Determination of whether a source is
operating in compliance with operation
and maintenance requirements will be
based on information available to the
Administrator which may include, but
is not limited to, monitoring results,
review of operation and maintenance
procedures, review of operation and
maintenance records, and inspection of
the source.
■ 4. Section 63.6120 is amended by
revising paragraphs (b) and (c) to read
as follows:
§ 63.6120 What performance tests and
other procedures must I use?
*
*
*
*
*
(b) Each performance test must be
conducted according to the
requirements in Table 3 of this subpart.
Before September 8, 2020, each
performance test must be conducted
according to the requirements of the
General Provisions at § 63.7(e)(1).
(c) Performance tests must be
conducted at high load, defined as 100
percent plus or minus 10 percent.
Before September 8, 2020, do not
conduct performance tests or
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13539
compliance evaluations during periods
of startup, shutdown, or malfunction.
After September 8, 2020, performance
tests shall be conducted under such
conditions based on representative
performance of the affected source for
the period being tested. Representative
conditions exclude periods of startup
and shutdown. The owner or operator
may not conduct performance tests
during periods of malfunction. The
owner or operator must record the
process information that is necessary to
document operating conditions during
the test and include in such record an
explanation to support that such
conditions represent normal operation.
Upon request, the owner or operator
shall make available to the
Administrator such records as may be
necessary to determine the conditions of
performance tests.
*
*
*
*
*
■ 5. Section 63.6125 is amended by
adding paragraph (e) to read as follows:
§ 63.6125 What are my monitor
installation, operation, and maintenance
requirements?
*
*
*
*
*
(e) After September 8, 2020, if you are
required to use a continuous monitoring
system (CMS), you must develop and
implement a CMS quality control
program that included written
procedures for CMS according to
§ 63.8(d)(1) through (2). You must keep
these written procedures on record for
the life of the affected source or until
the affected source is no longer subject
to the provisions of this part, to be made
available for inspection, upon request,
by the Administrator. If the performance
evaluation plan is revised, the owner or
operator shall keep previous (i.e.,
superseded) versions of the performance
evaluation plan on record to be made
available for inspection, upon request,
by the Administrator, for a period of 5
years after each revision to the plan. The
program of corrective action should be
included in the plan required under
§ 63.8(d)(2).
■ 6. Section 63.6140 is amended by
revising paragraph (c) to read as follows:
§ 63.6140 How do I demonstrate
continuous compliance with the emission
and operating limitations?
*
*
*
*
*
(c) Before September 8, 2020,
consistent with §§ 63.6(e) and 63.7(e)(1),
deviations that occur during a period of
startup, shutdown, and malfunction are
not violations if you have operated your
stationary combustion turbine in
accordance with § 63.6(e)(1)(i).
■ 7. Section 63.6150 is amended by:
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a. Revising paragraph (a) introductory
text, paragraph (a)(4) introductory text,
paragraph (c) introductory text, and
paragraph (e) introductory text, and
■ b. Adding paragraphs (a)(5), (f), (g), (h)
and (i).
The revisions and additions read as
follows:
■
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§ 63.6150
when?
What reports must I submit and
(a) Compliance report. Anyone who
owns or operates a stationary
combustion turbine which must meet
the emission limitation for
formaldehyde must submit a
semiannual compliance report
according to Table 6 of this subpart. The
semiannual compliance report must
contain the information described in
paragraphs (a)(1) through (5) of this
section. The semiannual compliance
report, including the excess emissions
and monitoring system performance
reports of § 63.10(e)(3), must be
submitted by the dates specified in
paragraphs (b)(1) through (5) of this
section, unless the Administrator has
approved a different schedule. After
September 8, 2020, or once the reporting
template has been available on the
Compliance and Emissions Data
Reporting Interface (CEDRI) website for
180 days, whichever date is later, you
must submit all subsequent reports to
the EPA following the procedure
specified in paragraph (g) of this
section.
*
*
*
*
*
(4) Before September 8, 2020, for each
deviation from an emission limitation,
the compliance report must contain the
information in paragraphs (a)(4)(i)
through (iii) of this section.
*
*
*
*
*
(5) After September 8, 2020, report
each deviation in the semiannual
compliance report. Report the
information specified in paragraphs
(a)(5)(i) through (iv) of this section.
(i) Report the number of deviations.
For each instance, report the start date,
start time, duration, and cause of each
deviation, and the corrective action
taken.
(ii) For each deviation, the report
must include a list of the affected
sources or equipment, an estimate of the
quantity of each regulated pollutant
emitted over any emission limit, a
description of the method used to
estimate the emissions.
(iii) Information on the number,
duration, and cause for monitor
downtime incidents (including
unknown cause, if applicable, other
than downtime associated with zero and
span and other daily calibration checks),
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as applicable, and the corrective action
taken.
(iv) Report the total operating time of
the affected source during the reporting
period.
*
*
*
*
*
(c) If you are operating as a stationary
combustion turbine which fires landfill
gas or digester gas equivalent to 10
percent or more of the gross heat input
on an annual basis, or a stationary
combustion turbine where gasified
MSW is used to generate 10 percent or
more of the gross heat input on an
annual basis, you must submit an
annual report according to Table 6 of
this subpart by the date specified unless
the Administrator has approved a
different schedule, according to the
information described in paragraphs
(d)(1) through (5) of this section. You
must report the data specified in (c)(1)
through (3) of this section. After
September 8, 2020, you must submit all
subsequent reports to the EPA following
the procedure specified in paragraph (g)
of this section.
*
*
*
*
*
(e) If you are operating a lean premix
gas-fired stationary combustion turbine
or a diffusion flame gas-fired stationary
combustion turbine as defined by this
subpart, and you use any quantity of
distillate oil to fire any new or existing
stationary combustion turbine which is
located at the same major source, you
must submit an annual report according
to Table 6 of this subpart by the date
specified unless the Administrator has
approved a different schedule,
according to the information described
in paragraphs (d)(1) through (5) of this
section. You must report the data
specified in (e)(1) through (3) of this
section. After September 8, 2020, you
must submit all subsequent reports to
the EPA following the procedure
specified in paragraph (g) of this
section.
*
*
*
*
*
(f) Performance test report. After
September 8, 2020, within 60 days after
the date of completing each
performance test required by this
subpart, you must submit the results of
the performance test (as specified in
§ 63.6145(f)) following the procedures
specified in paragraphs (f)(1) through (3)
of this section.
(1) Data collected using test methods
supported by the EPA’s Electronic
Reporting Tool (ERT) as listed on the
EPA’s ERT website (https://
www.epa.gov/electronic-reporting-airemissions/electronic-reporting-tool-ert)
at the time of the test. Submit the results
of the performance test to the EPA via
the CEDRI, which can be accessed
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Frm 00066
Fmt 4700
Sfmt 4700
through the EPA’s Central Data
Exchange (CDX) (https://cdx.epa.gov/).
The data must be submitted in a file
format generated through the use of the
EPA’s ERT. Alternatively, you may
submit an electronic file consistent with
the extensible markup language (XML)
schema listed on the EPA’s ERT
website.
(2) Data collected using test methods
that are not supported by the EPA’s ERT
as listed on the EPA’s ERT website at
the time of the test. The results of the
performance test must be included as an
attachment in the ERT or an alternate
electronic file consistent with the XML
schema listed on the EPA’s ERT
website. Submit the ERT generated
package or alternative file to the EPA via
CEDRI.
(3) Confidential business information
(CBI). If you claim some of the
information submitted under paragraph
(f)(1) of this section is CBI, you must
submit a complete file, including
information claimed to be CBI, to the
EPA. The file must be generated through
the use of the EPA’s ERT or an alternate
electronic file consistent with the XML
schema listed on the EPA’s ERT
website. Submit the file on a compact
disc, flash drive, or other commonly
used electronic storage medium and
clearly mark the medium as CBI. Mail
the electronic medium to U.S. EPA/
OAQPS/CORE CBI Office, Attention:
Group Leader, Measurement Policy
Group, MD C404–02, 4930 Old Page Rd.,
Durham, NC 27703. The same file with
the CBI omitted must be submitted to
the EPA via the EPA’s CDX as described
in paragraph (f)(1) of this section.
(g) If you are required to submit
reports following the procedure
specified in this paragraph, you must
submit reports to the EPA via CEDRI,
which can be accessed through the
EPA’s CDX (https://cdx.epa.gov/). You
must use the appropriate electronic
report template on the CEDRI website
(https://www.epa.gov/electronicreporting-air-emissions/complianceand-emissions-data-reporting-interfacecedri) for this subpart. The date report
templates become available will be
listed on the CEDRI website. The report
must be submitted by the deadline
specified in this subpart, regardless of
the method in which the report is
submitted. If you claim some of the
information required to be submitted via
CEDRI is CBI, submit a complete report,
including information claimed to be
CBI, to the EPA. The report must be
generated using the appropriate form on
the CEDRI website. Submit the file on a
compact disc, flash drive, or other
commonly used electronic storage
medium and clearly mark the medium
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Federal Register / Vol. 85, No. 46 / Monday, March 9, 2020 / Rules and Regulations
as CBI. Mail the electronic medium to
U.S. EPA/OAQPS/CORE CBI Office,
Attention: Group Leader, Measurement
Policy Group, MD C404–02, 4930 Old
Page Rd., Durham, NC 27703. The same
file with the CBI omitted must be
submitted to the EPA via the EPA’s CDX
as described earlier in this paragraph.
(h) If you are required to
electronically submit a report through
CEDRI in the EPA’s CDX, you may
assert a claim of EPA system outage for
failure to timely comply with the
reporting requirement. To assert a claim
of EPA system outage, you must meet
the requirements outlined in paragraphs
(h)(1) through (7) of this section.
(1) You must have been or will be
precluded from accessing CEDRI and
submitting a required report within the
time prescribed due to an outage of
either the EPA’s CEDRI or CDX systems.
(2) The outage must have occurred
within the period of time beginning five
business days prior to the date that the
submission is due.
(3) The outage may be planned or
unplanned.
(4) You must submit notification to
the Administrator in writing as soon as
possible following the date you first
knew, or through due diligence should
have known, that the event may cause
or has caused a delay in reporting.
(5) You must provide to the
Administrator a written description
identifying:
(i) The date(s) and time(s) when CDX
or CEDRI was accessed and the system
was unavailable;
(ii) A rationale for attributing the
delay in reporting beyond the regulatory
deadline to EPA system outage;
(iii) Measures taken or to be taken to
minimize the delay in reporting; and
(iv) The date by which you propose to
report, or if you have already met the
reporting requirement at the time of the
notification, the date you reported.
(6) The decision to accept the claim
of EPA system outage and allow an
extension to the reporting deadline is
solely within the discretion of the
Administrator.
(7) In any circumstance, the report
must be submitted electronically as
soon as possible after the outage is
resolved.
(i) If you are required to electronically
submit a report through CEDRI in the
EPA’s CDX, you may assert a claim of
force majeure for failure to timely
comply with the reporting requirement.
To assert a claim of force majeure, you
must meet the requirements outlined in
paragraphs (i)(1) through (5) of this
section.
(1) You may submit a claim if a force
majeure event is about to occur, occurs,
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16:34 Mar 06, 2020
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or has occurred or there are lingering
effects from such an event within the
period of time beginning five business
days prior to the date the submission is
due. For the purposes of this section, a
force majeure event is defined as an
event that will be or has been caused by
circumstances beyond the control of the
affected facility, its contractors, or any
entity controlled by the affected facility
that prevents you from complying with
the requirement to submit a report
electronically within the time period
prescribed. Examples of such events are
acts of nature (e.g., hurricanes,
earthquakes, or floods), acts of war or
terrorism, or equipment failure or safety
hazard beyond the control of the
affected facility (e.g., large scale power
outage).
(2) You must submit notification to
the Administrator in writing as soon as
possible following the date you first
knew, or through due diligence should
have known, that the event may cause
or has caused a delay in reporting.
(3) You must provide to the
Administrator:
(i) A written description of the force
majeure event;
(ii) A rationale for attributing the
delay in reporting beyond the regulatory
deadline to the force majeure event;
(iii) Measures taken or to be taken to
minimize the delay in reporting; and
(iv) The date by which you propose to
report, or if you have already met the
reporting requirement at the time of the
notification, the date you reported.
(4) The decision to accept the claim
of force majeure and allow an extension
to the reporting deadline is solely
within the discretion of the
Administrator.
(5) In any circumstance, the reporting
must occur as soon as possible after the
force majeure event occurs.
■ 8. Section 63.6155 is amended by
revising paragraph (a) introductory text
and paragraphs (a)(3) through (5) and
adding paragraphs (a)(6), (a)(7), and (d)
to read as follows:
§ 63.6155
(5) Records of all maintenance on the
air pollution control equipment as
required in § 63.10(b)(2)(iii).
(6) After September 8, 2020, records
of the date, time, and duration of each
startup period, recording the periods
when the affected source was subject to
the standard applicable to startup.
(7) After September 8, 2020, keep
records as follows.
(i) Record the number of deviations.
For each deviation, record the date,
time, cause, and duration of the
deviation.
(ii) For each deviation, record and
retain a list of the affected sources or
equipment, an estimate of the quantity
of each regulated pollutant emitted over
any emission limit and a description of
the method used to estimate the
emissions.
(iii) Record actions taken to minimize
emissions in accordance with
§ 63.6105(c), and any corrective actions
taken to return the affected unit to its
normal or usual manner of operation.
*
*
*
*
*
(d) Any records required to be
maintained by this part that are
submitted electronically via the EPA’s
CEDRI may be maintained in electronic
format. This ability to maintain
electronic copies does not affect the
requirement for facilities to make
records, data, and reports available
upon request to a delegated air agency
or the EPA as part of an on-site
compliance evaluation.
■ 9. Section 63.6170 is amended by
adding paragraph (c)(6) to read as
follows:
§ 63.6170 Who implements and enforces
this subpart?
*
*
*
*
*
(c) * * *
(6) Approval of an alternative to any
electronic reporting to the EPA required
by this subpart.
*
*
*
*
*
■ 10. Section 63.6175 is amended by
revising the definition for ‘‘Deviation’’
and adding a definition for ‘‘Startup’’ to
read as follows:
What records must I keep?
(a) You must keep the records as
described in paragraphs (a)(1) through
(7) of this section.
*
*
*
*
*
(3) Before September 8, 2020, records
of the occurrence and duration of each
startup, shutdown, or malfunction as
required in § 63.10(b)(2)(i).
(4) Before September 8, 2020, records
of the occurrence and duration of each
malfunction of the air pollution control
equipment, if applicable, as required in
§ 63.10(b)(2)(ii).
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Frm 00067
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§ 63.6175
subpart?
What definitions apply to this
*
*
*
*
*
Deviation means any instance in
which an affected source subject to this
subpart, or an owner or operator of such
a source:
(1) Fails to meet any requirement or
obligation established by this subpart,
including but not limited to any
emission limitation or operating
limitation;
(2) Fails to meet any term or condition
that is adopted to implement an
E:\FR\FM\09MRR1.SGM
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applicable requirement in this subpart
and that is included in the operating
permit for any affected source required
to obtain such a permit;
(3) Fails to meet any emission
limitation or operating limitation in this
subpart during malfunction, regardless
of whether or not such failure is
permitted by this subpart;
(4) Before September 8, 2020, fails to
satisfy the general duty to minimize
emissions established by § 63.6(e)(1)(i),
or
(5) After September 8, 2020, fails to
satisfy the general duty to minimize
emissions established by § 63.6105.
*
*
*
*
*
Startup begins at the first firing of fuel
in the stationary combustion turbine.
For simple cycle turbines, startup ends
when the stationary combustion turbine
has reached stable operation or after 1
hour, whichever is less. For combined
cycle turbines, startup ends when the
stationary combustion turbine has
reached stable operation or after 3
hours, whichever is less. Turbines in
combined cycle configurations that are
operating as simple cycle turbines must
meet the startup requirements for
simple cycle turbines while operating as
simple cycle turbines.
*
*
*
*
*
■ 11. Table 1 to Subpart YYYY of Part
63 is revised to read as follows:
Table 1 to Subpart YYYY of Part 63—
Emission Limitations
As stated in § 63.6100, you must
comply with the following emission
limitations.
For each new or reconstructed stationary combustion turbine described
in § 63.6100 which is . . .
You must meet the following emission limitations . . .
1. a lean premix gas-fired stationary combustion turbine as defined in
this subpart,
2. a lean premix oil-fired stationary combustion turbine as defined in
this subpart,
3. a diffusion flame gas-fired stationary combustion turbine as defined
in this subpart, or
4. a diffusion flame oil-fired stationary combustion turbine as defined in
this subpart.
limit the concentration of formaldehyde to 91 ppbvd or less at 15-percent O2, except during turbine startup. The period of time for turbine
startup is subject to the limits specified in the definition of startup in
§ 63.6175.
12. Table 2 to Subpart YYYY of Part
63 is revised to read as follows:
Table 2 to Subpart YYYY of Part 63—
Operating Limitations
As stated in §§ 63.6100 and 63.6140,
you must comply with the following
operating limitations.
■
For . . .
You must . . .
1. each stationary combustion turbine that is required to comply with
the emission limitation for formaldehyde and is using an oxidation
catalyst.
maintain the 4-hour rolling average of the catalyst inlet temperature
within the range suggested by the catalyst manufacturer. You are not
required to use the catalyst inlet temperature data that is recorded
during engine startup in the calculations of the 4-hour rolling average
catalyst inlet temperature.
maintain any operating limitations approved by the Administrator.
2. each stationary combustion turbine that is required to comply with
the emission limitation for formaldehyde and is not using an oxidation
catalyst.
13. Table 3 to Subpart YYYY of Part
63 is revised to read as follows:
Table 3 to Subpart YYYY of Part 63—
Requirements for Performance Tests
and Initial Compliance Demonstrations
■
for performance tests and initial
compliance demonstrations.
As stated in § 63.6120, you must
comply with the following requirements
You must . . .
Using . . .
According to the following requirements . . .
a. demonstrate formaldehyde emissions meet
the emission limitations specified in Table 1
by a performance test initially and on an annual basis AND.
Test Method 320 of 40 CFR part 63, appendix
A; ASTM D6348–12e1 1 provided that the
test plan preparation and implementation
provisions of Annexes A1 through A8 are
followed and the %R as determined in
Annex A5 is equal or greater than 70% and
less than or equal to 130%; 2 or other methods approved by the Administrator.
Method 1 or 1A of 40 CFR part 60, appendix
A.
formaldehyde concentration must be corrected to 15-percent O2, dry basis. Results
of this test consist of the average of the
three 1-hour runs. Test must be conducted
within 10 percent of 100-percent load.
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b. select the sampling port location and the
number of traverse points AND.
c. determine the O2 concentration at the sampling port location AND.
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Method 3A or 3B of 40 CFR part 60, appendix A; ANSI/ASME PTC 19.10–1981 1 (Part
10) manual portion only; ASTM D6522–11 1
if the turbine is fueled by natural gas.
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Fmt 4700
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if using an air pollution control device, the
sampling site must be located at the outlet
of the air pollution control device.
measurements to determine O2 concentration
must be made at the same time as the performance test.
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13543
You must . . .
Using . . .
According to the following requirements . . .
d. determine the moisture content at the sampling port location for the purposes of correcting the formaldehyde concentration to a
dry basis.
Method 4 of 40 CFR part 60, appendix A or
Test Method 320 of 40 CFR part 63, appendix A, or ASTM D6348–12e1 1.
measurements to determine moisture content
must be made at the same time as the performance test.
1 Incorporated
by reference, see § 63.14.
2 The %R value for each compound must be reported in the test report, and all field measurements must be corrected with the calculated %R
value for that compound using the following equation:
Reported Results = ((Measured Concentration in Stack)/(%R)) × 100.
14. Table 7 to Subpart YYYY of Part
63 is revised to read as follows:
■
Citation
Subject
Applies to subpart YYYY
§ 63.1 .................
General applicability of the
General Provisions.
Definitions ..............................
Yes .........................................................................................
Units and abbreviations .........
Prohibited activities ................
Construction and reconstruction.
Applicability ............................
Compliance dates for new
and reconstructed sources.
Notification .............................
[Reserved].
Compliance dates for new
and reconstructed area
sources that become major.
Compliance dates for existing
sources.
[Reserved].
Compliance dates for existing
area sources that become
major.
[Reserved].
General duty to minimize
emissions.
Yes.
Yes.
Yes.
§ 63.2 .................
§ 63.3 .................
§ 63.4 .................
§ 63.5 .................
§ 63.6(a) .............
§ 63.6(b)(1)–(4) ..
§ 63.6(b)(5) ........
§ 63.6(b)(6) ........
§ 63.6(b)(7) ........
§ 63.6(c)(1)–(2) ..
§ 63.6(c)(3)–(4) ..
§ 63.6(c)(5) .........
§ 63.6(d) .............
§ 63.6(e)(1)(i) .....
§ 63.6(e)(1)(ii) ....
§ 63.6(e)(1)(iii) ....
§ 63.6(e)(2) ........
§ 63.6(e)(3) ........
§ 63.6(f)(1) .........
§ 63.6(f)(2) .........
§ 63.6(f)(3) .........
§ 63.6(g)(1)–(3) ..
§ 63.6(h) .............
§ 63.6(i) ..............
§ 63.6(j) ..............
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Table 7 to Subpart YYYY of Part 63—
Applicability of General Provisions to
Subpart YYYY
You must comply with the applicable
General Provisions requirements:
§ 63.7(a)(1)–(2) ..
§ 63.7(a)(3) ........
§ 63.7(b)(1) ........
§ 63.7(b)(2) ........
VerDate Sep<11>2014
Requirement to correct malfunctions ASAP.
Operation and Maintenance
Requirements.
[Reserved].
SSMP .....................................
Applicability of standards except during startup, shutdown, or malfunction (SSM).
Methods for determining compliance.
Finding of compliance ............
Use of alternative standard ...
Opacity and visible emission
standards.
Yes .........................................................................................
Yes.
Yes.
Yes.
Yes.
Yes before September 8, 2020.
No after September 8, 2020. See § 63.6105 for general duty
requirement.
Yes before September 8, 2020.
No after September 8, 2020.
Yes.
Yes before September 8, 2020.
No after September 8, 2020.
Yes before September 8, 2020.
No after September 8, 2020.
Yes.
Yes.
Yes.
No ...........................................................................................
Yes.
Section 114 authority .............
Notification of performance
test.
Notification of rescheduling ...
Yes.
Yes.
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PO 00000
Additional terms defined in
§ 63.6175.
Additional terms defined in
§ 63.6175.
Yes.
Yes.
Compliance extension procedures and criteria.
Presidential compliance exemption.
Performance test dates .........
16:34 Mar 06, 2020
Explanation
Subpart YYYY does not contain opacity or visible emission standards.
Yes.
Yes .........................................................................................
Yes.
Frm 00069
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Subpart YYYY contains performance test dates at
§ 63.6110.
13544
Federal Register / Vol. 85, No. 46 / Monday, March 9, 2020 / Rules and Regulations
Citation
Subject
Applies to subpart YYYY
§ 63.7(c) .............
§ 63.7(d) .............
§ 63.7(e)(1) ........
Quality assurance/test plan ...
Testing facilities .....................
Conditions for conducting performance tests.
Conduct of performance tests
and reduction of data.
Test run duration ...................
Administrator may require
other testing under section
114 of the CAA.
Alternative test method provisions.
Performance test data analysis, recordkeeping, and reporting.
Waiver of tests .......................
Applicability of monitoring requirements.
Yes.
Yes.
Yes before September 8, 2020.
No after September 8, 2020.
Yes .........................................................................................
Performance specifications ....
[Reserved].
Monitoring for control devices
Monitoring ..............................
Multiple effluents and multiple
monitoring systems.
Monitoring system operation
and maintenance.
General duty to minimize
emissions and CMS operation.
Parts for repair of CMS readily available.
Requirement to develop SSM
Plan for CMS.
Monitoring system installation
Continuous monitoring system
(CMS) requirements.
Yes.
§ 63.7(e)(2) ........
§ 63.7(e)(3) ........
§ 63.7(e)(4) ........
§ 63.7(f) ..............
§ 63.7(g) .............
§ 63.7(h) .............
§ 63.8(a)(1) ........
§ 63.8(a)(2) ........
§ 63.8(a)(3) ........
§ 63.8(a)(4) ........
§ 63.8(b)(1) ........
§ 63.8(b)(2)–(3) ..
§ 63.8(c)(1) .........
§ 63.8(c)(1)(i) .....
§ 63.8(c)(1)(ii) .....
§ 63.8(c)(1)(iii) ....
§ 63.8(c)(2)–(3) ..
§ 63.8(c)(4) .........
Yes.
Yes.
Yes.
Yes .........................................................................................
Yes.
Yes before September 8, 2020.
No after September 8, 2020.
Yes.
Yes before September 8, 2020.
No after September 8, 2020.
Yes.
Yes .........................................................................................
No.
Yes .........................................................................................
§ 63.8(d)(1)–(2) ..
§ 63.8(d)(3) ........
CMS quality control ...............
Written procedures for CMS ..
§ 63.8(e) .............
CMS performance evaluation
Yes.
Yes before September 8, 2020.
No after September 8, 2020.
Yes .........................................................................................
§ 63.8(f)(1)–(5) ...
§ 63.8(f)(6) .........
Alternative monitoring method
Alternative to relative accuracy test.
Data reduction .......................
Yes.
Yes.
Applicability and State delegation of notification requirements.
Initial notifications ..................
Yes.
Request for compliance extension.
Notification of special compliance requirements for new
sources.
Notification of performance
test.
Notification of visible emissions/opacity test.
Yes.
Notification of performance
evaluation.
Yes.
§ 63.9(b)(1)–(5) ..
§ 63.9(c) .............
§ 63.9(d) .............
§ 63.9(e) .............
§ 63.9(f) ..............
§ 63.9(g)(1) ........
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16:34 Mar 06, 2020
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Subpart YYYY contains specific requirements for monitoring at § 63.6125.
No.
Yes.
Yes.
COMS minimum procedures
CMS requirements .................
§ 63.9(a) .............
Subpart YYYY specifies test
methods at § 63.6120.
Yes.
Yes.
§ 63.8(c)(5) .........
§ 63.8(c)(6)–(8) ..
§ 63.8(g) .............
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Explanation
Yes .........................................................................................
Yes .........................................................................................
Except that subpart YYYY
does not require continuous
opacity monitoring systems
(COMS).
Except that subpart YYYY
does not require COMS.
Except for § 63.8(e)(5)(ii),
which applies to COMS.
Except that provisions for
COMS are not applicable.
Averaging periods for demonstrating compliance are
specified at §§ 63.6135 and
63.6140.
Except that § 63.9(b)(3) is reserved.
Yes.
Yes.
No ...........................................................................................
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Subpart YYYY does not contain opacity or VE standards.
Federal Register / Vol. 85, No. 46 / Monday, March 9, 2020 / Rules and Regulations
Citation
Subject
Explanation
Subpart YYYY does not contain opacity or VE standards.
Notification of use of COMS
data.
No ...........................................................................................
§ 63.9(g)(3) ........
Notification that criterion for
alternative to relative accuracy test audit (RATA) is
exceeded.
Notification of compliance status.
Yes.
Adjustment of submittal deadlines.
Change in previous information.
Administrative provisions for
recordkeeping and reporting.
Record retention ....................
Recordkeeping of occurrence
and duration of startups
and shutdowns.
Recordkeeping of failures to
meet a standard.
Yes.
§ 63.9(i) ..............
§ 63.9(j) ..............
§ 63.10(a) ...........
§ 63.10(b)(1) ......
§ 63.10(b)(2)(i) ...
§ 63.10(b)(2)(ii) ..
§ 63.10(b)(2)(iii) ..
§ 63.10(b)(2)(iv)–
(v).
§ 63.10(b)(2)(vi)–
(xi).
§ 63.10(b)(2)(xii)
§ 63.10(b)(2)(xiii)
§ 63.10(b)(2)(xiv)
§ 63.10(b)(3) ......
§ 63.10(c)(1)–
(14).
§ 63.10(c)(15) .....
§ 63.10(d)(1) ......
§ 63.10(d)(2) ......
§ 63.10(d)(3) ......
§ 63.10(d)(4) ......
§ 63.10(d)(5) ......
Maintenance records .............
Records related to actions
during SSM.
CMS records ..........................
Record when under waiver ....
Records when using alternative to RATA.
Records of supporting documentation.
Records of applicability determination.
Additional records for sources
using CMS.
Use of SSM Plan ...................
General reporting requirements.
Report of performance test
results.
Reporting opacity or VE observations.
Yes .........................................................................................
Yes.
Yes.
Yes before September 8, 2020.
No after September 8, 2020.
Yes before September 8, 2020.
No after September 8, 2020. See § 63.6155 for recordkeeping of (1) date, time and duration; (2) listing of affected source or equipment, and an estimate of the quantity of each regulated pollutant emitted over the standard;
and (3) actions to minimize emissions and correct the failure.
Yes.
Yes before September 8, 2020.
No after September 8, 2020.
Yes.
Yes.
Yes.
Yes.
Yes.
Yes .........................................................................................
Yes.
No ...........................................................................................
COMS-related report .............
No ...........................................................................................
§ 63.10(e)(3) ......
Excess emissions and parameter exceedances reports.
Yes .........................................................................................
§ 63.10(e)(4) ......
Reporting COMS data ...........
No ...........................................................................................
§ 63.10(f) ............
Waiver for recordkeeping and
reporting.
Flares .....................................
State authority and delegations.
Yes.
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16:34 Mar 06, 2020
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Except that § 63.10(c)(2)–(4)
and (9) are reserved.
Yes before September 8, 2020.
No after September 8, 2020.
Yes.
Yes.
No. After September 8, 2020, see 63.6150(a) for malfunction reporting requirements.
Yes.
§ 63.11 ...............
§ 63.12 ...............
Except that notifications for
sources not conducting performance tests are due 30
days after completion of
performance evaluations.
§ 63.9(h)(4) is reserved.
Yes.
Progress reports ....................
Startup, shutdown, and malfunction reports.
Additional CMS reports ..........
§ 63.10(e)(1) and
(2)(i).
§ 63.10(e)(2)(ii) ..
jbell on DSKJLSW7X2PROD with RULES
Applies to subpart YYYY
§ 63.9(g)(2) ........
§ 63.9(h) .............
13545
No.
Yes.
Frm 00071
Fmt 4700
Sfmt 4700
E:\FR\FM\09MRR1.SGM
09MRR1
Subpart YYYY does not contain opacity or VE standards.
Subpart YYYY does not require COMS.
After September 8, 2020 submitted with the compliance
report through CEDRI according to § 63.6150(a).
Subpart YYYY does not require COMS.
13546
Federal Register / Vol. 85, No. 46 / Monday, March 9, 2020 / Rules and Regulations
Citation
Subject
Applies to subpart YYYY
§ 63.13 ...............
Addresses ..............................
Yes .........................................................................................
§ 63.14 ...............
§ 63.15 ...............
Incorporation by reference .....
Availability of information .......
Yes.
Yes.
[FR Doc. 2020–02714 Filed 3–6–20; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2018–0571; FRL–10003–94]
Chrysodeixis includens;
Nucleopolyhedrovirus Isolate #460;
Exemption From the Requirement of a
Tolerance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
jbell on DSKJLSW7X2PROD with RULES
I. General Information
This regulation establishes an
exemption from the requirement of a
tolerance for residues of Chrysodeixis
includens nucleopolyhedrovirus isolate
#460 in or on all food commodities
when used in accordance with label
directions and good agricultural
practices. AgBiTech Pty Ltd. submitted
a petition to EPA under the Federal
Food, Drug, and Cosmetic Act (FFDCA),
requesting an exemption from the
requirement of a tolerance. This
regulation eliminates the need to
establish a maximum permissible level
for residues of Chrysodeixis includens
nucleopolyhedrovirus isolate #460 in or
on all food commodities under FFDCA.
DATES: This regulation is effective
March 9, 2020. Objections and requests
for hearings must be received on or
before May 8, 2020 and must be filed in
accordance with the instructions
provided in 40 CFR part 178 (see also
Unit I.C. of the SUPPLEMENTARY
INFORMATION).
ADDRESSES: The docket for this action,
identified by docket identification (ID)
number EPA–HQ–OPP–2018–0571, is
available at https://www.regulations.gov
or at the Office of Pesticide Programs
Regulatory Public Docket (OPP Docket)
in the Environmental Protection Agency
Docket Center (EPA/DC), West William
Jefferson Clinton Bldg., Rm. 3334, 1301
Constitution Ave. NW, Washington, DC
20460–0001. The Public Reading Room
is open from 8:30 a.m. to 4:30 p.m.,
Monday through Friday, excluding legal
holidays. The telephone number for the
SUMMARY:
VerDate Sep<11>2014
16:34 Mar 06, 2020
Jkt 250001
Public Reading Room is (202) 566–1744,
and the telephone number for the OPP
Docket is (703) 305–5805. Please review
the visitor instructions and additional
information about the docket available
at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT:
Robert McNally, Biopesticides and
Pollution Prevention Division (7511P),
Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave. NW, Washington, DC
20460–0001; main telephone number:
(703) 305–7090; email address:
BPPDFRNotices@epa.gov.
SUPPLEMENTARY INFORMATION:
A. Does this action apply to me?
You may be potentially affected by
this action if you are an agricultural
producer, food manufacturer, or
pesticide manufacturer. The following
list of North American Industrial
Classification System (NAICS) codes is
not intended to be exhaustive, but rather
provides a guide to help readers
determine whether this document
applies to them. Potentially affected
entities may include:
• Crop production (NAICS code 111).
• Animal production (NAICS code
112).
• Food manufacturing (NAICS code
311).
• Pesticide manufacturing (NAICS
code 32532).
B. How can I get electronic access to
other related information?
You may access a frequently updated
electronic version of 40 CFR part 180
through the Government Publishing
Office’s e-CFR site at https://
www.ecfr.gov/cgi-bin/textidx?&c=ecfr&tpl=/ecfrbrowse/Title40/
40tab_02.tpl.
C. How can I file an objection or hearing
request?
Under FFDCA section 408(g), 21
U.S.C. 346a(g), any person may file an
objection to any aspect of this regulation
and may also request a hearing on those
objections. You must file your objection
or request a hearing on this regulation
in accordance with the instructions
PO 00000
Frm 00072
Fmt 4700
Sfmt 4700
Explanation
After September 8, 2020 not
applicable to reports required to be submitted
through CEDRI by
63.6150(c), (e), (f), or (g).
provided in 40 CFR part 178. To ensure
proper receipt by EPA, you must
identify docket ID number EPA–HQ–
OPP–2018–0571 in the subject line on
the first page of your submission. All
objections and requests for a hearing
must be in writing and must be received
by the Hearing Clerk on or before May
8, 2020. Addresses for mail and hand
delivery of objections and hearing
requests are provided in 40 CFR
178.25(b).
In addition to filing an objection or
hearing request with the Hearing Clerk
as described in 40 CFR part 178, please
submit a copy of the filing (excluding
any Confidential Business Information
(CBI)) for inclusion in the public docket.
Information not marked confidential
pursuant to 40 CFR part 2 may be
disclosed publicly by EPA without prior
notice. Submit the non-CBI copy of your
objection or hearing request, identified
by docket ID number EPA–HQ–OPP–
2018–0571, by one of the following
methods:
• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the online
instructions for submitting comments.
Do not submit electronically any
information you consider to be CBI or
other information whose disclosure is
restricted by statute.
• Mail: OPP Docket, Environmental
Protection Agency Docket Center (EPA/
DC), (28221T), 1200 Pennsylvania Ave.
NW, Washington, DC 20460–0001.
• Hand Delivery: To make special
arrangements for hand delivery or
delivery of boxed information, please
follow the instructions at https://
www.epa.gov/dockets/contacts.html.
Additional instructions on
commenting or visiting the docket,
along with more information about
dockets generally, is available at https://
www.epa.gov/dockets.
II. Background
In the Federal Register of December
21, 2018 (83 FR 65660) (FRL–9985–67),
EPA issued a notice pursuant to FFDCA
section 408(d)(3), 21 U.S.C. 346a(d)(3),
announcing the filing of a pesticide
tolerance exemption petition (PP
7F8641) by AgBiTech Pty Ltd., 8 Rocla
Ct., Glenvale, Queensland 4350,
Australia (c/o MacIntosh & Associates,
E:\FR\FM\09MRR1.SGM
09MRR1
Agencies
[Federal Register Volume 85, Number 46 (Monday, March 9, 2020)]
[Rules and Regulations]
[Pages 13524-13546]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2020-02714]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 63
[EPA-HQ-OAR-2017-0688; FRL-10005-14-OAR]
RIN 2060-AT00
National Emission Standards for Hazardous Air Pollutants:
Stationary Combustion Turbines Residual Risk and Technology Review
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This action finalizes the residual risk and technology review
(RTR) conducted for the Stationary Combustion Turbines source category
regulated under national emission standards for hazardous air
pollutants (NESHAP). In addition, we are taking final action addressing
requirements during periods of startup, shutdown, and malfunction (SSM)
and to add electronic reporting requirements. The EPA is finalizing our
proposed determination that the risks from this source category due to
emissions of air toxics are acceptable and that the existing NESHAP
provides an ample margin of safety to protect public health. The EPA is
also finalizing our proposed determination that we identified no new
cost-effective controls under the technology review that would achieve
further emissions reductions from the source category.
DATES: This final rule is effective on March 9, 2020. The incorporation
by reference (IBR) of certain publications listed in the rule is
approved by the Director of the Federal Register as of March 9, 2020.
ADDRESSES: The U.S. Environmental Protection Agency (EPA) has
established a docket for this action under Docket ID No. EPA-HQ-OAR-
2017-0688. All documents in the docket are listed on the https://www.regulations.gov/ website. Although listed, some information is not
publicly available, e.g., confidential business information or other
information whose disclosure is restricted by statute. Certain other
material, such as copyrighted material, is not placed on the internet
and will be publicly available only in hard copy form. Publicly
available docket materials are available either electronically through
https://www.regulations.gov/, or in hard copy at the EPA Docket Center,
WJC West Building, Room Number 3334, 1301 Constitution Ave. NW,
Washington, DC. The Public Reading Room hours of operation are 8:30
a.m. to 4:30 p.m. Eastern Standard Time (EST), Monday through Friday.
The telephone number for the Public Reading Room is (202) 566-1744, and
the telephone number for the EPA Docket Center is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: For questions about this final action,
contact Melanie King, Sector Policies and Programs Division (D243-01),
Office of Air Quality Planning and Standards, U.S. Environmental
Protection Agency, Research Triangle Park, North Carolina 27711;
telephone number: (919) 541-2469; fax number: (919) 541-4991; and email
address: [email protected]. For specific information regarding the
risk modeling methodology, contact Mark Morris, Health and
Environmental Impacts Division (C539-02), Office of Air Quality
Planning and Standards, U.S. Environmental Protection Agency, Research
Triangle Park, North Carolina 27711; telephone number: (919) 541-5416;
and email address: [email protected]. For information about the
applicability of the Stationary Combustion Turbines NESHAP to a
particular entity, contact Sara Ayres, Office of Enforcement and
Compliance Assurance, U.S. Environmental Protection Agency, 77 West
Jackson Boulevard (Mail Code E-19J), Chicago, Illinois 60604; telephone
number: (312) 353-6266; and email address: [email protected].
SUPPLEMENTARY INFORMATION:
Preamble acronyms and abbreviations. We use multiple acronyms and
terms in this preamble. While this list may not be exhaustive, to ease
the reading of this preamble and for reference purposes, the EPA
defines the following terms and acronyms here:
ANSI American National Standards Institute
ASME American Society of Mechanical Engineers
BACT best available control technology
CAA Clean Air Act
CAER Combined Air Emissions Reporting
CDX Central Data Exchange
CEDRI Compliance and Emissions Data Reporting Interface
CEMS continuous emissions monitoring systems
CFR Code of Federal Regulations
CMS continuous monitoring system
EPA Environmental Protection Agency
ERT Electronic Reporting Tool
FTIR Fourier transform infrared
HAP hazardous air pollutants(s)
HQ hazard quotient
IBR incorporation by reference
km kilometer
LAER lowest achievable emission rate
MACT maximum achievable control technology
MIR maximum individual risk
NAICS North American Industry Classification System
NESHAP national emission standards for hazardous air pollutants
NOx oxides of nitrogen
NTTAA National Technology Transfer and Advancement Act
O2 oxygen
OMB Office of Management and Budget
PB-HAP hazardous air pollutant known to be persistent and bio-
accumulative in the environment
ppbvd parts per billion by volume, dry basis
PRA Paperwork Reduction Act
PTC performance test code
RACT reasonably available control technology
[[Page 13525]]
RBLC RACT/BACT/LAER Clearinghouse
REL recommended exposure limit
RFA Regulatory Flexibility Act
RTR residual risk and technology review
SCR selective catalytic reduction
SSM startup, shutdown, and malfunction
TOSHI target organ-specific hazard index
tpy tons per year
UMRA Unfunded Mandates Reform Act
U.S. United States
U.S.C. United States Code
v. versus
VCS voluntary consensus standard
XML extensible markup language
Background information. On April 12, 2019, the EPA proposed the RTR
for the Stationary Combustion Turbines NESHAP as well as amendments
addressing periods of SSM and requiring electronic reporting. In this
action, we are finalizing certain decisions and revisions for the rule.
We summarize some of the more significant comments we timely received
regarding the proposed rule and provide our responses in this preamble.
A summary of all other public comments on the proposal and the EPA's
responses to those comments is available in the National Emission
Standards for Hazardous Air Pollutants from Stationary Combustion
Turbines (40 CFR part 63, subpart YYYY), Residual Risk and Technology
Review, Final Amendments, Summary of Public Comments and Responses on
Proposed Rule, Docket ID No. EPA-HQ-OAR-2017-0688. A ``track changes''
version of the regulatory language that incorporates the changes in
this action is available in the docket.
At this time, the EPA is not finalizing the proposed removal of the
administrative stay of the effectiveness of the standards for new lean
premix and diffusion flame gas-fired turbines to allow for additional
time to review the public comments on the proposed removal of the stay,
as well as a petition to delist the Stationary Combustion Turbines
source category that was filed in August 2019. This final rule does not
include responses to comments on lifting the stay. The EPA is still
reviewing the comments on lifting the stay and will respond to them in
any subsequent action.
Organization of this document. The information in this preamble is
organized as follows:
I. General Information
A. Does this action apply to me?
B. Where can I get a copy of this document and other related
information?
C. Judicial Review and Administrative Reconsideration
II. Background
A. What is the statutory authority for this action?
B. What is the Stationary Combustion Turbines source category
and how does the NESHAP regulate HAP emissions from the source
category?
C. What changes did we propose for the Stationary Combustion
Turbines source category in our April 12, 2019, proposal?
III. What is included in this final rule?
A. What are the final rule amendments based on the risk review
for the Stationary Combustion Turbines source category?
B. What are the final rule amendments based on the technology
review for the Stationary Combustion Turbines source category?
C. What are the final rule amendments addressing emissions
during periods of SSM?
D. What other changes have been made to the NESHAP?
E. What are the effective and compliance dates of the standards?
IV. What is the rationale for our final decisions and amendments for
the Stationary Combustion Turbines source category?
A. Residual Risk Review for the Stationary Combustion Turbines
Source Category
B. Technology Review for the Stationary Combustion Turbines
Source Category
C. SSM for the Stationary Combustion Turbines Source Category
D. Electronic Reporting Requirements for the Stationary
Combustion Turbines Source Category
V. Summary of Cost, Environmental, and Economic Impacts and
Additional Analyses Conducted
A. What are the affected facilities?
B. What are the air quality impacts?
C. What are the cost impacts?
D. What are the economic impacts?
E. What are the benefits?
F. What analysis of environmental justice did we conduct?
G. What analysis of children's environmental health did we
conduct?
VI. Statutory and Executive Order Reviews
A. Executive Orders 12866: Regulatory Planning and Review and
Executive Order 13563: Improving Regulation and Regulatory Review
B. Executive Order 13771: Reducing Regulations and Controlling
Regulatory Costs
C. Paperwork Reduction Act (PRA)
D. Regulatory Flexibility Act (RFA)
E. Unfunded Mandates Reform Act (UMRA)
F. Executive Order 13132: Federalism
G. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
H. Executive Order 13045: Protection of Children From
Environmental Health Risks and Safety Risks
I. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
J. National Technology Transfer and Advancement Act (NTTAA) and
1 CFR Part 51
K. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low-Income
Populations
L. Congressional Review Act (CRA)
I. General Information
A. Does this action apply to me?
Regulated entities. Categories and entities potentially regulated
by this action are shown in Table 1 of this preamble.
Table 1--NESHAP and Industrial Source Categories Affected by This Final
Action
------------------------------------------------------------------------
NESHAP and source category NAICS \1\ code
------------------------------------------------------------------------
Stationary Combustion Turbines......... 2211, 486210, 211111, 211113,
221.
------------------------------------------------------------------------
\1\ North American Industry Classification System.
Table 1 of this preamble is not intended to be exhaustive, but
rather to provide a guide for readers regarding entities likely to be
affected by the final action for the source category listed. To
determine whether your facility is affected, you should examine the
applicability criteria in the appropriate NESHAP. If you have any
questions regarding the applicability of any aspect of this NESHAP,
please contact the appropriate person listed in the preceding FOR
FURTHER INFORMATION CONTACT section of this preamble.
B. Where can I get a copy of this document and other related
information?
In addition to being available in the docket, an electronic copy of
this final action will also be available on the internet. Following
signature by the EPA Administrator, the EPA will post a copy of this
final action at: https://www.epa.gov/stationary-sources-air-pollution/stationary-combustion-turbines-national-emission-standards. Following
publication in the Federal Register, the EPA will post the Federal
[[Page 13526]]
Register version and key technical documents at this same website.
Additional information is available on the RTR website at https://www.epa.gov/stationary-sources-air-pollution/risk-and-technology-review-national-emissions-standards-hazardous. This information
includes an overview of the RTR program and links to project websites
for the RTR source categories.
C. Judicial Review and Administrative Reconsideration
Under Clean Air Act (CAA) section 307(b)(1), judicial review of the
final actions is available only by filing a petition for review in the
United States Court of Appeals for the District of Columbia Circuit
(the court) by May 8, 2020. Under CAA section 307(b)(2), the
requirements established by this final rule may not be challenged
separately in any civil or criminal proceedings brought by the EPA to
enforce the requirements.
Section 307(d)(7)(B) of the CAA further provides that only an
objection to a rule or procedure which was raised with reasonable
specificity during the period for public comment (including any public
hearing) may be raised during judicial review. This section also
provides a mechanism for the EPA to reconsider the rule if the person
raising an objection can demonstrate to the Administrator that it was
impracticable to raise such objection within the period for public
comment or if the grounds for such objection arose after the period for
public comment (but within the time specified for judicial review) and
if such objection is of central relevance to the outcome of the rule.
Any person seeking to make such a demonstration should submit a
Petition for Reconsideration to the Office of the Administrator, U.S.
EPA, Room 3000, EPA WJC South Building, 1200 Pennsylvania Ave. NW,
Washington, DC 20460, with a copy to both the person(s) listed in the
preceding FOR FURTHER INFORMATION CONTACT section, and the Associate
General Counsel for the Air and Radiation Law Office, Office of General
Counsel (Mail Code 2344A), U.S. EPA, 1200 Pennsylvania Ave. NW,
Washington, DC 20460.
II. Background
A. What is the statutory authority for this action?
Section 112 of the CAA establishes a two-stage regulatory process
to address emissions of hazardous air pollutants (HAP) from stationary
sources. In the first stage, we must identify categories of sources
emitting one or more of the HAP listed in CAA section 112(b) and then
promulgate technology-based NESHAP for those sources. ``Major sources''
are those that emit, or have the potential to emit, any single HAP at a
rate of 10 tons per year (tpy) or more, or 25 tpy or more of any
combination of HAP. For major sources, these standards are commonly
referred to as maximum achievable control technology (MACT) standards
and must reflect the maximum degree of emission reductions of HAP
achievable (after considering cost, energy requirements, and non-air
quality health and environmental impacts). In developing MACT
standards, CAA section 112(d)(2) directs the EPA to consider the
application of measures, processes, methods, systems, or techniques,
including, but not limited to those that reduce the volume of or
eliminate HAP emissions through process changes, substitution of
materials, or other modifications; enclose systems or processes to
eliminate emissions; collect, capture, or treat HAP when released from
a process, stack, storage, or fugitive emissions point; are design,
equipment, work practice, or operational standards; or any combination
of the above.
For these MACT standards, the statute specifies certain minimum
stringency requirements, which are referred to as MACT floor
requirements, and which may not be based on cost considerations. See
CAA section 112(d)(3). For new sources, the MACT floor cannot be less
stringent than the emission control achieved in practice by the best-
controlled similar source. The MACT standards for existing sources can
be less stringent than floors for new sources, but they cannot be less
stringent than the average emission limitation achieved by the best-
performing 12 percent of existing sources in the category or
subcategory (or the best-performing five sources for categories or
subcategories with fewer than 30 sources). In developing MACT
standards, we must also consider control options that are more
stringent than the floor under CAA section 112(d)(2). We may establish
standards more stringent than the floor, based on the consideration of
the cost of achieving the emissions reductions, any non-air quality
health and environmental impacts, and energy requirements.
In the second stage of the regulatory process, the CAA requires the
EPA to undertake two different analyses, which we refer to as the
technology review and the residual risk review. Under the technology
review, we must review the technology-based standards and revise them
``as necessary (taking into account developments in practices,
processes, and control technologies)'' no less frequently than every 8
years, pursuant to CAA section 112(d)(6). Under the residual risk
review, we must evaluate the risk to public health remaining after
application of the technology-based standards and revise the standards,
if necessary, to provide an ample margin of safety to protect public
health or to prevent, taking into consideration costs, energy, safety,
and other relevant factors, an adverse environmental effect. The
residual risk review is required within 8 years after promulgation of
the technology-based standards, pursuant to CAA section 112(f). In
conducting the residual risk review, if the EPA determines that the
current standards provide an ample margin of safety to protect public
health, it is not necessary to revise the MACT standards pursuant to
CAA section 112(f).\1\ For more information on the statutory authority
for this rule, see 84 FR 15046.
---------------------------------------------------------------------------
\1\ The court has affirmed this approach of implementing CAA
section 112(f)(2)(A): NRDC v. EPA, 529 F.3d 1077, 1083 (DC Cir.
2008) (``If EPA determines that the existing technology-based
standards provide an `ample margin of safety,' then the Agency is
free to readopt those standards during the residual risk
rulemaking.'').
---------------------------------------------------------------------------
B. What is the Stationary Combustion Turbines source category and how
does the NESHAP regulate HAP emissions from the source category?
The EPA promulgated the Stationary Combustion Turbines NESHAP on
March 5, 2004 (69 FR 10512). The standards are codified at 40 CFR part
63, subpart YYYY, and apply to stationary combustion turbines at major
sources of HAP. The stationary combustion turbine industry consists of
facilities that own and operate stationary combustion turbines. The
source category covered by this MACT standard currently includes 243
facilities. Stationary combustion turbines are typically located at
power plants, compressor stations, landfills and industrial facilities
such as chemical plants.
Stationary combustion turbines have been divided into the following
eight subcategories: (1) Emergency stationary combustion turbines, (2)
stationary combustion turbines which burn landfill or digester gas
equivalent to 10 percent or more of the gross heat input on an annual
basis or where gasified municipal solid waste is used to generate 10
percent or more of the gross heat input to the stationary combustion
turbine on an annual basis, (3) stationary combustion turbines of less
than 1 megawatt rated peak power output, (4) stationary lean premix
combustion turbines when firing gas
[[Page 13527]]
and when firing oil at sites where all turbines fire oil no more than
an aggregate total of 1,000 hours annually (also referred to herein as
``lean premix gas-fired turbines''), (5) stationary lean premix
combustion turbines when firing oil at sites where all turbines fire
oil more than an aggregate total of 1,000 hours annually (also referred
to herein as ``lean premix oil-fired turbines''), (6) stationary
diffusion flame combustion turbines when firing gas and when firing oil
at sites where all turbines fire oil no more than an aggregate total of
1,000 hours annually (also referred to herein as ``diffusion flame gas-
fired turbines''), (7) stationary diffusion flame combustion turbines
when firing oil at sites where all turbines fire oil more than an
aggregate total of 1,000 hours annually (also referred to herein as
``diffusion flame oil-fired turbines''), and (8) stationary combustion
turbines operated on the North Slope of Alaska (defined as the area
north of the Arctic Circle (latitude 66.5 degrees North)).
The sources of emissions are the exhaust gases from combustion of
gaseous and liquid fuels in a stationary combustion turbine. The HAP
that are present in the exhaust gases from stationary combustion
turbines include formaldehyde, toluene, benzene, and acetaldehyde.
Metallic HAP are present in the exhaust from distillate oil-fired
turbines; these metallic HAP are generally carried over from the fuel
constituents.
The NESHAP requires new or reconstructed stationary combustion
turbines in the lean premix gas-fired, lean premix oil-fired, diffusion
flame gas-fired, and diffusion flame oil-fired subcategories to meet a
formaldehyde limit of 91 parts per billion by volume, dry basis (ppbvd)
at 15-percent oxygen (O2). Compliance is demonstrated
through initial and annual performance testing and continuous
monitoring of operating parameters. The requirements of the rule are
currently under a stay of effectiveness for new lean premix and
diffusion flame gas-fired turbines.
C. What changes did we propose for the Stationary Combustion Turbines
source category in our April 12, 2019, proposal?
On April 12, 2019, the EPA published a proposed rule in the Federal
Register for the Stationary Combustion Turbines NESHAP, 40 CFR part 63,
subpart YYYY, that took into consideration the RTR analyses. In the
proposed rule, we proposed to find that risks from the Stationary
Combustion Turbines source category due to emissions of air toxics are
acceptable and that the existing NESHAP provides an ample margin of
safety to protect public health. No new cost-effective controls were
identified in the technology review for the proposed rule. The EPA also
proposed to eliminate the exemption for periods of SSM, and our risk
analysis assumed removal of that exemption. We proposed a new
requirement to electronically submit performance test results and
semiannual compliance reports. Finally, we proposed to remove the stay
of the standards for new lean premix and diffusion flame gas-fired
turbines. We did not propose any revisions to the emission standards
based on our RTR.
III. What is included in this final rule?
This action finalizes the EPA's determinations pursuant to the RTR
provisions of CAA section 112 for the Stationary Combustion Turbines
source category. This action also finalizes other changes to the
NESHAP, including amendments to the SSM provisions and the addition of
electronic reporting requirements. This action reflects changes to the
April 19, 2019, proposal in consideration of comments received during
the public comment period described in section IV of this preamble.
As stated previously, the EPA is not finalizing the proposed
removal of the stay of the effectiveness of the standards for new lean
premix and diffusion flame gas-fired turbines at this time. The EPA
received numerous comments on the proposed stay indicating that 180
days is not sufficient time for owners and operators to conduct all of
the activities that are needed for their turbines to come into
compliance with the standards, which include the design, procurement,
and installation of emission controls and parametric monitoring
equipment that can fit within existing sites (as compared to new
facilities where the controls are incorporated into the facility
design), performance testing, and implementation of procedures for
monitoring, recordkeeping, and reporting. More time is needed to review
these comments on the removal of the stay. In addition, the EPA
received a petition to delist the Stationary Combustion Turbines source
category from regulation under CAA section 112 in August 2019. As
discussed in more detail in the April 12, 2019, proposal, the EPA
proposed to delist certain subcategories of stationary combustion
turbines in 2004 under CAA section 112(c)(9)(B) and stayed the
effectiveness of the standards for those subcategories, pending the
outcome of the proposed delisting. A subsequent 2007 decision by the
court \2\ held that the EPA has no authority to delist subcategories
under CAA section 112(c)(9)(B). Consequently, the EPA proposed to
remove the stay in the April 12, 2019, proposal. In recognition of the
EPA's inability to delist subcategories under CAA section 112(c)(9)(B),
the new August 2019 petition requests delisting of the entire
Stationary Combustion Turbines source category and provides an
assessment of the risks for the entire source category. A copy of the
petition is in the docket for this rulemaking (Docket ID No. EPA-HQ-
OAR-2017-0688). The EPA is in the process of reviewing the petition and
has not made a determination regarding whether the information included
in the petition supports delisting the entire source category, but
notes that the petitioners provided an analysis of the risks from the
source category and, based on their analysis, the petitioners concluded
that a demonstration can be made that delisting is appropriate under
CAA section 112(c)(9)(B). The EPA has determined that it would be
reasonable to delay taking final action on the stay until we have made
a determination regarding the source category delisting petition, so
that turbine owners and operators do not make expenditures on emission
controls and performance testing that will not be required if the
source category is delisted. Such expenditures would be wasteful and
unwarranted if the source category is delisted. Moreover, the EPA has
no legal obligation to lift the stay in this RTR rulemaking. Although
the EPA often uses the RTR rulemaking vehicle to revise or update
various aspects of a NESHAP, as it did here with respect to its
proposal to eliminate a stay provision in the rule, the EPA did not do
so nor is the EPA required to do so under CAA section 112(d)(6) or
(f)(4).
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\2\ NRDC v. EPA, 489 F.3d 1364 (D.C. Cir. 2007).
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A. What are the final rule amendments based on the risk review for the
Stationary Combustion Turbines source category?
We are finalizing our proposed finding that risks remaining after
implementation of the existing MACT standards for this source category
(as revised in this action to remove the SSM exemption) are acceptable.
We are also finalizing our proposed determination that the current
NESHAP (as revised in this action to remove the SSM exemption) provides
an ample margin of safety to protect public health. Therefore, we are
not finalizing any revisions to the numerical emission
[[Page 13528]]
limits based on these analyses conducted under CAA section 112(f).
B. What are the final rule amendments based on the technology review
for the Stationary Combustion Turbines source category?
We determined that there are no developments in practices,
processes, and control technologies that warrant revisions to the MACT
standards for this source category. Therefore, we are not finalizing
revisions to the MACT standards under CAA section 112(d)(6).
C. What are the final rule amendments addressing emissions during
periods of SSM?
In its 2008 decision in Sierra Club v. EPA, 551 F.3d 1019 (D.C.
Cir. 2008), the court vacated portions of two provisions in the EPA's
CAA section 112 regulations governing the emissions of HAP during
periods of SSM. Specifically, the court vacated the SSM exemption
contained in 40 CFR 63.6(f)(1) and 40 CFR 63.6(h)(1), holding that
under section 302(k) of the CAA, emissions standards or limitations
must be continuous in nature and that the SSM exemption violates the
CAA's requirement that some CAA section 112 standards apply
continuously.
We have eliminated the SSM exemption in this rule. Consistent with
Sierra Club v. EPA, the EPA has established standards in this rule that
apply at all times. We have also revised Table 7 (the General
Provisions applicability table) in several respects as is explained in
more detail in the proposal. For example, we have eliminated the
incorporation of the General Provisions' requirement that the source
develop an SSM plan. We have also eliminated and revised certain
recordkeeping and reporting requirements that are related to the SSM
exemption as described in detail in the proposed rule and in section
IV.C of this preamble.
D. What other changes have been made to the NESHAP?
The EPA is requiring owners and operators of stationary combustion
turbine facilities to submit electronic copies of certain required
performance test results and semiannual compliance reports through the
EPA's Central Data Exchange (CDX) using the Compliance and Emissions
Data Reporting Interface (CEDRI). The final rule requires that
performance test results collected using test methods that are
supported by the EPA's Electronic Reporting Tool (ERT) as listed on the
ERT website \3\ at the time of the test be submitted in the format
generated through the use of the ERT and that other performance test
results be submitted in portable document format using the attachment
module of the ERT. The test methods required by 40 CFR part 63, subpart
YYYY that are currently supported by the ERT are EPA Methods 3A and 4
of 40 CFR part 60, appendix A. For periodic compliance reports, the
final rule requires that owners and operators use the appropriate
spreadsheet template to submit information to CEDRI. The final version
of the template for these reports is located on the CEDRI website.\4\
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\3\ https://www.epa.gov/electronic-reporting-air-emissions/electronic-reporting-tool-ert.
\4\ https://www.epa.gov/electronic-reporting-air-emissions/compliance-and-emissions-data-reporting-interface-cedri.
---------------------------------------------------------------------------
The electronic submittal of the reports addressed in this
rulemaking will increase the usefulness of the data contained in those
reports, is in keeping with current trends in data availability and
transparency, will further assist in the protection of public health
and the environment, will improve compliance by facilitating the
ability of regulated facilities to demonstrate compliance with
requirements and by facilitating the ability of delegated state, local,
tribal, and territorial air agencies and the EPA to assess and
determine compliance, and will ultimately reduce burden on regulated
facilities, delegated air agencies, and the EPA. Electronic reporting
also eliminates paper-based, manual processes, thereby saving time and
resources, simplifying data entry, eliminating redundancies, minimizing
data reporting errors, and providing data quickly and accurately to the
affected facilities, air agencies, the EPA, and the public. For a more
thorough discussion of electronic reporting, see the memorandum,
Electronic Reporting Requirements for New Source Performance Standards
(NSPS) and National Emission Standards for Hazardous Air Pollutants
(NESHAP) Rules, available in Docket ID No. EPA-HQ-OAR-2017-0688.
E. What are the effective and compliance dates of the standards?
The revisions to the MACT standards being promulgated in this
action are effective on March 9, 2020. The compliance date for affected
sources to comply with the amendments pertaining to SSM and electronic
reporting is 180 days after the effective date of the final rule. As
discussed elsewhere in this preamble, we are adding a requirement that
performance test results and semiannual compliance reports be submitted
electronically, and we are changing the requirements for periods of SSM
by removing the exemption from the requirement to meet the emission
standards during periods of SSM and promulgating an operational
standard for startup. Our experience with similar industries that are
required to convert reporting mechanisms to install necessary hardware
and software, become familiar with the process of submitting
performance test results and compliance reports electronically through
the EPA's CEDRI, test these new electronic submission capabilities, and
reliably employ electronic reporting shows that a time period of a
minimum of 90 days and, more typically, 180 days, is generally
necessary to successfully accomplish these revisions. Our experience
with similar industries further shows that this sort of regulated
facility generally requires a time period of 180 days to read and
understand the amended rule requirements; to evaluate their operations
to ensure that they can meet the standards during periods of startup
and shutdown as defined in the rule and make any necessary adjustments;
and to update their operation, maintenance, and monitoring plans to
reflect the revised requirements. The EPA recognizes the confusion that
multiple different compliance dates for individual requirements would
create and the additional burden such an assortment of dates would
impose. From our assessment of the timeframe needed for compliance with
the entirety of the revised requirements, the EPA considers a period of
180 days to be the most expeditious compliance period practicable and,
thus, is requiring that affected sources must be in compliance with all
of the revised requirements within 180 days of the regulation's
effective date. All affected facilities would have to continue to meet
the current requirements of 40 CFR part 63, subpart YYYY, until the
applicable compliance date of the amended rule.
IV. What is the rationale for our final decisions and amendments for
the Stationary Combustion Turbines source category?
For each issue, this section provides a description of what we
proposed and what we are finalizing for the issue, the EPA's rationale
for the final decisions and amendments, and a summary of key comments
and responses. For all comments not discussed in this preamble, comment
summaries and the EPA's responses can be found in the comment summary
and response document available in the docket.
[[Page 13529]]
A. Residual Risk Review for the Stationary Combustion Turbines Source
Category
1. What did we propose pursuant to CAA section 112(f) for the
Stationary Combustion Turbines source category?
Pursuant to CAA section 112(f), the EPA conducted a residual risk
review and presented the results of this review, along with our
proposed decisions regarding risk acceptability and ample margin of
safety, in the April 12, 2019, proposed rule for 40 CFR part 63,
subpart YYYY (84 FR 15046). The results of the risk assessment for the
proposal are presented briefly below in Table 2 of this preamble. More
detail is in the residual risk technical support document, Residual
Risk Assessment for the Stationary Combustion Turbines Source Category
in Support of the 2019 Risk and Technology Review Proposed Rule,
available in the docket for this rulemaking (Docket ID No. EPA-HQ-OAR-
2017-0688).
Table 2--Stationary Combustion Turbines Inhalation Risk Assessment Results
--------------------------------------------------------------------------------------------------------------------------------------------------------
Maximum individual Population at increased Annual cancer incidence Maximum chronic Maximum screening acute noncancer
cancer risk (in 1 risk of cancer >=1-in-1 (cases per year) noncancer TOSHI 3 HQ 4
million) 2 million ----------------------------------------------------------------------------------------
Number of ---------------------------------------------------- Based on . . . Based on . . .
facilities Based on . . . Based on . . . ----------------------------------------------------
1 ----------------------------------------------------
Actual Allowable Actual Allowable Actual Allowable Actual Allowable Based on actual emissions level
emissions emissions emissions emissions emissions emissions emissions emissions
level level level level level level level level
--------------------------------------------------------------------------------------------------------------------------------------------------------
253 3 3 42,000 42,000 0.04 0.04 0.04 0.04 HQREL = 2 (acrolein), HQAEGL-1 =
0.07
--------------------------------------------------------------------------------------------------------------------------------------------------------
\1\ Number of facilities evaluated in the risk analysis.
\2\ Maximum individual excess lifetime cancer risk due to HAP emissions from the source category.
\3\ Maximum target organ specific hazard index (TOSHI). The target organ system with the highest TOSHI for the source category is respiratory. The
respiratory TOSHI was calculated using the California Environmental Protection Agency chronic recommended exposure limit (REL) for acrolein. The EPA
is in the process of updating the Integrated Risk Information System reference concentration for acrolein.
\4\ The maximum estimated acute exposure concentration was divided by available short-term threshold values to develop an array of hazard quotient (HQ)
values. HQ values shown use the lowest available acute threshold value, which in most cases is the REL. When an HQ exceeds 1, we also show the HQ
using the next lowest available acute dose-response value.
The results of the proposal inhalation risk modeling using actual
and allowable emissions data, as shown in Table 2 of this preamble,
indicate that the maximum lifetime individual cancer risk (MIR) is 3-
in-1 million, the maximum chronic noncancer TOSHI is 0.04, and the
maximum screening acute noncancer HQ (off-facility site) is 2 (driven
by acrolein). Only one facility has an HQ (REL) that exceeds 1. At
proposal, the total annual cancer incidence (national) from these
facilities was estimated to be 0.04 excess cancer cases per year, or
one case in every 25 years. The facility-wide maximum lifetime cancer
MIR was estimated to be 2,000-in-1 million at proposal, driven by
ethylene oxide emissions from chemical manufacturing. At proposal, the
total estimated cancer incidence from whole facility emissions was
estimated to be 0.7 excess cancer cases per year, or one excess case in
every 1 to 2 years. Approximately 2.8 million people were estimated to
have cancer risks above 1-in-1 million from exposure to HAP emitted
from both MACT and non-MACT sources at the facilities in the source
category. The estimated maximum chronic noncancer TOSHI based on
facility-wide emissions is 4 (respiratory), driven by emissions of
chlorine from chemical manufacturing, and approximately 360 people are
exposed to a TOSHI above 1.
At proposal, potential multipathway human health risks were
estimated using a three-tier screening assessment of the persistent
bio-accumulative HAP (PB-HAP) emitted by facilities in this source
category. The only pollutants with elevated Tier 1 and Tier 2 screening
values were arsenic (cancer), cadmium (noncancer), and mercury
(noncancer). The Tier 3 screening values for these pollutants were low.
For cancer, the Tier 3 screening value for arsenic was 4. For
noncancer, the Tier 3 screening value for cadmium was less than 1, and
the screening value for mercury was 1.
Several environmental HAP are emitted by sources within this source
category: Arsenic, dioxins/furans, and polycyclic organic matter.
Therefore, at proposal we conducted a three-tier screening assessment
of the potential adverse environmental risks associated with emissions
of these pollutants. Based on this assessment (through Tier 2), there
were no exceedances of any of the ecological benchmarks evaluated for
any of the pollutants, and we proposed that we do not expect an adverse
environmental effect as a result of HAP emissions from this source
category.
We weighed all health risk factors, including those shown in Table
2 of this preamble, in our risk acceptability determination and
proposed that the residual risks from the Stationary Combustion
Turbines source category are acceptable (section IV.B.1 of proposal
preamble, 84 FR 15062, April 12, 2019). We then considered whether 40
CFR part 63, subpart YYYY provides an ample margin of safety to protect
public health and prevents, taking into consideration costs, energy,
safety, and other relevant factors, an adverse environmental effect. In
considering whether the standards should be tightened to provide an
ample margin of safety to protect public health, we considered all
health factors evaluated in the risk assessment and evaluated the cost
and feasibility of available control technologies and other measures
(including the controls, measures, and costs reviewed under the
technology review) that could be applied to this source category to
further reduce the risks (or potential risks) due to emissions of HAP
identified in our risk assessment. In this analysis, we considered the
results of the technology review, risk assessment, and other aspects of
our MACT rule review to determine whether there are any emission
reduction measures necessary to provide an ample margin of safety with
respect to the risks associated with these emissions. Our risk analysis
indicated the risks from the source category are low for both cancer
and noncancer health effects, and, therefore, any risk reductions from
further available control options would result in minimal health
benefits. Moreover, as noted in our discussion of the technology
review, no additional cost-effective measures were identified for
reducing HAP emissions from affected sources in the Stationary
Combustion Turbines source category. Thus, we determined that the
current Stationary Combustion Turbines NESHAP provides an ample margin
of safety to protect public health.
Our technology review focused on identifying developments in
practices, processes, and control technologies that
[[Page 13530]]
have occurred since the Stationary Combustion Turbines NESHAP was
originally promulgated in 2004. Our review of the developments in
technology for the Stationary Combustion Turbines source category did
not reveal any changes that require revisions to the emission
standards. The only add-on HAP emission control technology identified
in the original NESHAP rulemaking was an oxidation catalyst. No new or
improved add-on control technologies that reduce HAP emissions from
turbines were identified during the technology review. Our review also
did not identify any new or improved operation and maintenance
practices, process changes, pollution prevention approaches, or testing
and monitoring techniques for stationary combustion turbines.
Therefore, we determined that no revisions are necessary pursuant to
CAA section 112(d)(6).
2. How did the risk review change for the Stationary Combustion
Turbines source category?
The only change in the risk assessment for the final rule is that
the EPA modeled an additional 46 turbines that were identified in a
public comment (Docket ID Item No. EPA-HQ-OAR-2017-0688-0116) as
subject to the Stationary Combustion Turbines NESHAP. The emissions
data used to model those additional turbines and the results of the
modeling are discussed in the memorandum titled Emissions Data Used in
Modeling Files for Additional Turbines for Stationary Combustion
Turbines Risk and Technology Review (RTR), which is in the docket for
this rulemaking (Docket ID No. EPA-HQ-OAR-2017-0688). The modeling
input files are also available in the docket. The risks for the
additional turbines were all lower than the risks for the turbines
modeled for the proposed rule, so the additional risk analysis did not
result in changes to our proposed decisions on risk acceptability,
ample margin of safety, and adverse environmental effect.
3. What key comments did we receive on the risk review, and what are
our responses?
We received comments in support of and against the proposed
residual risk review and our determination that no revisions were
warranted under CAA section 112(f)(2) for the Stationary Combustion
Turbines source category. Generally, the comments that were not
supportive of the determination from the risk review suggested changes
to the underlying risk assessment methodology. For example, some
commenters stated that the EPA should lower the acceptability benchmark
so that risks below 100-in-1 million are unacceptable, include
emissions outside of the source categories in question in the risk
assessment, and assume that pollutants with noncancer health risks have
no safe level of exposure. After review of all the comments received,
we determined that no changes were necessary. The comments and our
specific responses can be found in the document, National Emission
Standards for Hazardous Air Pollutants from Stationary Combustion
Turbines (40 CFR part 63, subpart YYYY) Residual Risk and Technology
Review, Final Amendments: Summary of Public Comments and Responses on
Proposed Rule, available in the docket for this action (Docket ID No.
EPA-HQ-OAR-2017-0688).
4. What is the rationale for our final approach and final decisions for
the risk review?
As noted in our proposal, the EPA sets standards under CAA section
112(f)(2) using a two-step standard-setting approach, with an
analytical first step to make a risk-acceptability determination that
considers all health information, including risk estimation
uncertainty, and includes a presumptive limit on MIR of approximately
1-in-10 thousand (see 54 FR 38045, September 14, 1989). We weigh all
health risk factors in our risk acceptability determination, including
the cancer MIR, cancer incidence, the maximum cancer TOSHI, the maximum
acute noncancer HQ, the extent of noncancer risks, the distribution of
cancer and noncancer risks in the exposed population, and the risk
estimation uncertainties.
Since proposal, neither the risk assessment nor our determinations
regarding risk acceptability, ample margin of safety, or adverse
environmental effects have changed, even considering the additional 46
turbines modeled. Therefore, for the reasons explained in the proposed
rule, we determined that the risks from this source category are
acceptable, and the current standards provide an ample margin of safety
to protect public health and prevent an adverse environmental effect.
Therefore, we are not revising this subpart to require additional
controls pursuant to CAA section 112(f)(2) based on the residual risk
review, and we are readopting the existing standards under CAA section
112(f)(2).
B. Technology Review for the Stationary Combustion Turbines Source
Category
1. What did we propose pursuant to CAA section 112(d)(6) for the
Stationary Combustion Turbines source category?
Pursuant to CAA section 112(d)(6), we conducted a technology
review, which focused on identifying and evaluating developments in
practices, processes, and control technologies for control of HAP
emissions from stationary combustion turbines. No cost-effective
developments in practices, processes, or control technologies were
identified in our technology review to warrant revisions to the
standards. More information concerning our technology review can be
found in the Technology Review for Stationary Combustion Turbines Risk
and Technology Review (RTR) memorandum, which is in the docket for this
action (Docket ID No. EPA-HQ-OAR-2017-0688), and in the preamble for
the proposed rule (84 FR 15046).
2. How did the technology review change for the Stationary Combustion
Turbines source category?
The technology review has not changed since the proposal.
3. What key comments did we receive on the technology review, and what
are our responses?
We received both supportive and adverse comments on the proposed
technology review. Most commenters supported the EPA's proposed
technology review determination. The summarized comments and the EPA's
responses are provided in the National Emission Standards for Hazardous
Air Pollutants from Stationary Combustion Turbines (40 CFR part 63,
subpart YYYY), Residual Risk and Technology Review, Final Amendments,
Summary of Public Comments and Responses on Proposed Rule document
referenced in section IV.A.3 of the preamble. The most significant
adverse comments and the EPA's responses are also provided below.
Comment: One commenter stated that the EPA reviewed only the
technology used to limit formaldehyde in the technology review and does
not evaluate selective catalytic reduction (SCR) or any other of the
technologies identified as ``developments'' within the meaning of CAA
section 112(d)(6), which is unlawful and arbitrary.
The commenter stated that the EPA ignored other HAP controls in the
technology review--such as wet controls (water or steam injection),
lean premixed combustion, and SCR--without any rational explanation.
The
[[Page 13531]]
commenter noted that the EPA is aware of evidence showing that SCR can
and does reduce HAP, such as benzene. The commenter cited a 2016 study,
Catalytic Destruction of a Surrogate Organic Hazardous Air Pollutant as
a Potential Co-benefit for Coal-fired Selective Catalyst Reduction
Systems (C.W. Lee et al.), which found that ``significant destruction
of benzene occurred under a broad range of SCR operating conditions,
suggesting that a large number of coalfired utility boilers which are
equipped with SCR for NOX control have potential to achieve
reduction of organic HAP emissions as a co-benefit.''
The commenter stated that the EPA must consider ways to reduce
emissions through developments such as: Methods to assure more
efficient use of turbines; use of lower HAP fuels; and/or alternative
energy generation altogether through renewables and/or battery storage
systems. According to the commenter, the EPA must consider battery
storage in particular because this has the potential to increase
efficiency and reduce emissions, and to reduce all of the turbine-based
risks the EPA found to zero by reducing the emissions completely if
paired with a renewable energy source such as solar. The commenter
stated that the EPA does not evaluate or take into account any of these
developments, and this is unlawful, arbitrary, and capricious under CAA
section 112(d)(6).
The commenter noted that there are also developments in volatile
organic compounds, acid gas, and metal controls, leak detection and
repair, and monitoring that the EPA must consider and ensure that the
standards ``tak[e] into account'' for this source category and these
facilities. The commenter stated that since the EPA finalized the
original standards, the EPA has recognized such developments in other
contexts. The commenter concluded that the EPA would violate CAA
section 112(d)(6) by failing to consider and account for the
``developments'' in fenceline monitoring, leak detection and repair,
and pollution controls--particularly where data show significant health
risks from a range of emitted pollutants, including cancer, chronic
noncancer, and acute risk. The commenter stated that refusing to
consider these developments is also arbitrary. The commenter explained
that many facilities that include turbines are similar to refineries,
in their significant potential for leaks and emission spikes that cause
health and safety threats, and in their complexity. The commenter
concluded that all of the developments discussed are readily available,
would improve emission control, reduce health risks and refusing to
consider them and revise the standards to ``account'' for them would be
unlawful and arbitrary.
Conversely, another commenter stated that, setting aside whether
fenceline monitoring technology constitutes a ``development'' under CAA
section 112(d)(6), it would be arbitrary and capricious to adopt
fenceline monitoring requirements for stationary combustion turbines as
part of this RTR. Fenceline monitoring is used to identify sources of
fugitive emissions. According to the commenter, stationary combustion
turbines do not have fugitive HAP emissions. According to the
commenter, even if some combustion turbine facilities may also contain
other equipment with the potential for fugitive emissions, such as
natural gas transmission pipelines, that other equipment is not part of
the source category under review here and cannot be the basis for new
requirements adopted pursuant to CAA section 112(d)(6) review for
combustion turbines.
Response: The EPA disagrees with the commenter that it only
reviewed technologies used to limit formaldehyde emissions. As
discussed in the memorandum, Technology Review for Stationary
Combustion Turbines Risk and Technology Review (RTR) (Docket ID Item
No. EPA-HQ-OAR-2017-0688-0066), the EPA reviewed a variety of sources
of information during the technology review. Those sources of
information included the EPA's RACT/BACT/LAER Clearinghouse (RBLC),
construction and operating permits for stationary combustion turbines,
information provided by owners and operators of stationary combustion
turbines, and manufacturers of emission control technologies and
testing equipment. The review was not limited to technologies that
limit formaldehyde emissions, as evidenced by the RBLC search criteria
documented in Appendix A of the memorandum and the questions asked of
industry stakeholders described in Appendix B of the memorandum.
The 2016 study cited by the commenter as evidence that SCR reduces
HAP such as benzene evaluated the HAP reductions from SCR applied to
simulated coal combustion flue gases. The chemical composition of the
coal combustion flue gases is very different from the chemical
composition of the exhaust from stationary combustion turbines, and
there is no evidence provided that the use of SCR in coal combustion
exhaust and the resulting catalytic chemical reactions that cause the
destruction of benzene would occur in the same way if SCR is applied to
stationary combustion turbines. The information provided to the EPA
regarding ``dual-purpose'' catalysts that include SCR for nitrogen
oxides (NOx) removal and oxidation for carbon monoxide (CO) and HAP
removal indicates that the HAP reduction occurs due to the oxidation
and not from the SCR.\5\ The commenter did not provide any evidence
that water or steam injection would reduce HAP emissions, or that fuels
that lead to lower HAP emissions have been developed. Lean premix
combustion is not a new technology (and is one of the subcategories
established in the original 2004 40 CFR part 63, subpart YYYY
rulemaking) and the commenter did not provide any evidence that there
have been any developments in the technology. As discussed in the
memorandum cited above, the trade organization representing gas turbine
manufacturers indicated that there have not been any changes in turbine
design since the 2004 rulemaking. We disagree that the EPA must
consider alternative energy generation altogether through renewables
and/or battery storage and that the use of batteries if paired with
renewable energy such as solar would reduce emissions completely. The
commenter's suggested technology (renewables and batteries) is not a
revision to the emissions standard for the Stationary Combustion
Turbines source category, which is what the EPA is required to review
and revise as appropriate, under CAA section 112(d)(6). The commenter
is suggesting elimination of combustion turbines as a source category
and that is beyond the scope of this rulemaking. Even if such an
approach were an appropriate ``revision'' of the emission standards for
combustion turbines under CAA section 112(d)(6), the commenter did not
provide any information to show that using renewables or battery
storage has been demonstrated on the scale that would be needed to
replace the generation produced by the combustion turbines subject to
subpart YYYY.
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\5\ See the memorandum, Technology Review for Stationary
Combustion Turbines Risk and Technology Review (RTR) (Docket ID Item
No. EPA-HQ-OAR-2017-0688-0066).
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Regarding the comment that the EPA should consider leak detection
and repair and fenceline monitoring requirements, the EPA notes that
those requirements were included in the NESHAP for Petroleum Refineries
(40 CFR part 63, subpart CC). Those requirements for refineries target
refinery MACT-regulated fugitive emission sources (e.g., storage tanks,
[[Page 13532]]
equipment leaks, and wastewater). Fenceline monitoring, as discussed in
the preamble to the proposed Petroleum Refinery rule (79 FR 36920), may
identify significant increases in emissions, but small increases in
emissions are unlikely to impact the fenceline concentrations.
Fenceline monitoring would not be beneficial for the Stationary
Combustion Turbines source category because stationary turbines have
very low fugitive HAP emissions and their operation does not involve
storage and transport of large volumes of volatile organic materials
unlike the refinery sector. The potential for fugitive volatile organic
HAP emissions, as a result of the reduced amount of transport and the
reduced storage of volatile organic materials, is vastly lower.
4. What is the rationale for our final approach for the technology
review?
We evaluated all of the comments on the EPA's technology review and
determined that no changes to the review are needed based on the
comments. For the reasons explained in the proposed rule, we determined
that no cost-effective developments in practices, processes, or control
technologies were identified in our technology review to warrant
revisions to the standards. More information concerning our technology
review and how we evaluate cost effectiveness can be found in the
Technology Review for Stationary Combustion Turbines Risk and
Technology Review (RTR) memorandum, which is in the docket for this
action (Docket ID No. EPA-HQ-OAR-2017-0688), and in the preamble for
the proposed rule (84 FR 15046). Therefore, pursuant to CAA section
112(d)(6), we are finalizing our technology review as proposed.
C. SSM Provisions for the Stationary Combustion Turbines Source
Category
1. What did we propose for the Stationary Combustion Turbines source
category?
In its 2008 decision in Sierra Club v. EPA, 551 F.3d 1019 (D.C.
Cir. 2008), the court vacated portions of two provisions in the EPA's
CAA section 112 General Provisions regulations governing the emissions
of HAP during periods of SSM. Specifically, the court vacated the SSM
exemption contained in 40 CFR 63.6(f)(1) and 40 CFR 63.6(h)(1), holding
that under section 302(k) of the CAA, emissions standards or
limitations must be continuous in nature and that the SSM exemption
violates the CAA's requirement that some CAA section 112 standards
apply continuously.
The EPA proposed to revise provisions related to SSM that are not
consistent with the requirement that standards apply at all times. More
information concerning our proposal on SSM can be found in the proposed
rule (84 FR 15046). As discussed in the proposal, the EPA proposed an
operational standard in lieu of a numeric emission limit during periods
of startup, in accordance with CAA section 112(h). The EPA proposed
that during turbine startup, owners and operators must minimize the
turbine's time spent at idle or holding at low load levels and minimize
the turbine's startup time to a period needed for appropriate and safe
loading of the turbine, not to exceed 1 hour for simple cycle
stationary combustion turbines and 3 hours for combined cycle
stationary combustion turbines, after which time the formaldehyde
emission limitation of 91 ppbvd at 15-percent O2 would
apply. We did not propose a different standard that would apply during
shutdown.
2. How did the SSM provisions change for the Stationary Combustion
Turbines source category?
In the final rule, we revised aspects of the operational standard
for startup from the proposal based on public comments. We removed the
language specifying that the owner or operator must minimize the
turbine's time spent at idle or holding at low levels and minimize the
turbine's startup time to a period needed for appropriate and safe
loading of the turbine. We have also added a definition for startup
that is specific to stationary combustion turbines, rather than using
the general definition in the General Provisions (subpart A) of 40 CFR
part 63. The definition specifies that startup begins at the first
firing of fuel in the stationary combustion turbine.
In response to comments regarding the proposed operational standard
for startup and the proposed conclusion that a standard for shutdown is
not necessary, the EPA evaluated Acid Rain Program hourly emissions
data for stationary combustion turbines from 2018.\6\ The stabilization
of NOx emissions, an indicator of stable combustion and post-combustion
processes, was used to determine startup and shutdown times for
turbines subject to 40 CFR part 63, subpart YYYY. Based on the Acid
Rain Program emissions data, the EPA determined that the majority of
turbine startup times were less than 1 hour for simple cycle turbines
and the majority of startup times were less than 3 hours for combined
cycle turbines. Upper prediction limits for the best performers for
startup time were also determined following statistical methods used to
define upper prediction limits for MACT emission standards (e.g.,
methods detailed in the memorandum, CO CEMS MACT Floor Analysis August
2012 for the Industrial, Commercial, and Institutional Boilers and
Process Heaters National Emission Standards for Hazardous Air
Pollutants Major Source, Docket ID Item No. EPA-HQ-OAR-2002-0058-3877).
Upper prediction limits were less than 1 hour for simple cycle turbines
and less than 3 hours for combined cycle turbines regardless of startup
type (i.e., cold, warm, and hot starts). Additionally, the majority of
shutdown times were less than 30 minutes for both simple cycle and
combined cycle turbines. Finally, utilizing oxidation catalyst had
minimal effect on startup and shutdown times.
---------------------------------------------------------------------------
\6\ See the memorandum titled Stationary combustion turbine
startups and shutdowns based on Acid Rain Program CEMS data, which
can be found in the rulemaking docket (Docket ID No. EPA-HQ-OAR-
2017-0688).
---------------------------------------------------------------------------
3. What key comments did we receive on the SSM provisions, and what are
our responses?
Comment: Commenters stated that the proposed rule does not define
what constitutes the period of startup, including the beginning and the
ending. The commenters added that 40 CFR part 63 defines startup as
``the setting in operation of an affected source or portion of an
affected source for any purpose.'' The commenters stated that this
definition is vague and does not specify when startup ends. The
commenters suggested that the EPA provide a definition of startup as it
applies to simple cycle and combined cycle combustion turbines. A
commenter also stated that some combined cycle combustion turbines can
operate in simple cycle mode. Therefore, the EPA also needs to address
these types of turbines in the definitions or the standard itself,
according to the commenter. A commenter added that the definition used
in the standard should not interfere with the definition of startup in
other parts of the CAA or in operating permits, nor should it constrain
normal operations. The commenter specifically suggested that the EPA
revise the operational standard to apply only upon the first firing of
fuel in the combustion turbine.
Response: The EPA agrees with the commenters that it would be
appropriate to define startup as beginning at the first firing of fuel
in the stationary combustion turbine and to
[[Page 13533]]
specify when the startup standard ends. The EPA has specified different
startup times for simple cycle and combined cycle turbines, as
discussed elsewhere in this section. For simple cycle turbines, the EPA
has specified in the final rule that startup ends when the stationary
combustion turbine has reached stable operation or after 1 hour,
whichever is less. For combined cycle turbines, startup ends when the
stationary combustion turbine has reached stable operation or after 3
hours, whichever is less. If a turbine in a combined cycle
configuration is operating as a simple cycle turbine, it must follow
the requirements for simple cycle turbines. Regarding the comment that
the definition should not interfere with the definition of startup in
other parts of the CAA or in operating permits or constrain normal
operations, the EPA does not anticipate any interference. As discussed
elsewhere in this section, the standard is based on turbine startup
times gathered from emissions data, and it also allows the turbine to
take longer to start up if needed (while requiring that the turbine
meet the applicable formaldehyde limit).
Comment: Many commenters expressed support for the establishment of
the operational standard during startup operations but asserted that
the EPA must allow more time for certain startup operations for
combined cycle stationary combustion turbines. Some commenters stated
that they believe the record does not demonstrate the feasibility of a
3-hour startup time for combined cycle units. They added that it
appears the 3-hour limit was taken from a document from the Gas Turbine
Association (Docket ID Item No. EPA-HQ-OAR-2017-0688-0033). These
commenters stated that while this document discusses a period of 3
hours for startup, the document also discusses the wide range of
variability in the time needed. Several commenters explained that the
startup time for a combined cycle turbine is impacted by its
integration with other site facilities and the type of startup. Some
commenters cited specific instances when additional startup time beyond
what was proposed for combined cycle turbines may be expected,
including:
Startups following extended downtime or a unit turnaround
which commenters asserted may take up to 10 hours. A commenter provided
a list of nine major steps for startup following a unit turnaround in
their comment letter to support the need for additional startup time;
startup involving combined heat and power units as the
startup typically involves purging and setup of the heat recovery steam
generator, followed by gas speed-up and loading, followed by the steam
turbine speedup and loading;
various types of startup including a ``warm'' start (i.e.,
when the steam turbine first stage or reheat inner metal temperature is
between 400 and 700 degrees Fahrenheit) and a ``cold'' start (i.e.,
when the steam turbine first stage or reheat inner metal temperature is
less than 400 degrees Fahrenheit). One commenter reviewed operating
data from 2017-2019 for some of its stationary combined cycle
combustion turbines, noting that 32 out of 82 ``warm'' startups
exceeded a 3-hour duration with an average duration of 3.3-4 hours, and
all 23 of the ``cold'' startups exceeded the 3-hour duration with an
average duration of 5-6 hours. Another commenter stated that member
companies will be submitting facility-specific data showing the impact
of startup type on duration;
startup involving gas fuel turbines integrated with other
systems associated with multiple boilers to produce electricity and
steam for a large manufacturing complex; and
pre-startup commissioning activities and initial startup
at liquid natural gas terminals.
These commenters suggested that the EPA provide additional time in the
startup operational standard for combined cycle turbines.
Some commenters suggested that 4 hours be provided in the standard.
Other commenters suggested that the EPA allow 5.5 hours as the baseline
with provisions for site-specific requests for additional time. Some
commenters suggested that the final action should provide a procedure
for the EPA or state permitting authorities to provide application of
an alternative standard for combined cycle turbines if an operator
demonstrates that it is needed. A commenter suggested that the EPA
allow between 6-8 hours in the standard. Another commenter suggested
that the EPA allow up to 10 hours in the standard. One commenter
suggested that, consistent with their state operating permit
requirements and due to the unique nature of their operations, the EPA
should allow up to 12 hours in the standard. Another commenter added
that the EPA could provide different time frames if they differentiated
between different startup types (i.e., provide the most time for cold
startups and the least time for hot startups).
Alternatively, other commenters suggested that the EPA could
maintain the 3-hour standard for combined cycle turbines but allow a
more extended startup time to facilities if they document the need for
the additional startup time; maintain associated records; provide semi-
annual reporting; and take steps during the startup to minimize
emissions consistent with good air pollution control practices.
Commenters suggested the standard should require that owners and
operators of combined cycle units minimize the time the turbines spend
at idle or low load operations, and that they complete the startup
process while operating the equipment in a manner consistent with good
air pollution control practices for minimizing emissions, rather than
having the EPA impose a one-size-fits-all hour limit. One commenter
suggested that the end of the startup period should be when the unit
begins to operate in ``normal mode'' as signaled from the turbine
control system. Commenters also suggested that if the EPA maintains an
hour limit, the standard should be amended to exclude malfunctions
encountered during startup from the calculation of the startup time as
such events could cause sources to exceed the window.
One commenter recommended that the final rule not supersede site-
specific requirements with a one-size-fits-all approach. The commenter
suggested that the final standard include approved procedural work
practices to provide additional assurance of an efficient and
expeditious startup process (i.e., a procedural startup work practice
could specify that ammonia injection would begin when the catalyst
temperature meets a certain minimum temperature). According to the
commenter, these procedural work practices can be maintained,
submitted, and approved by the administrator outside of the air permit
to minimize permit changes similar to the way quality assurance/quality
control manuals are handled.
One commenter suggested that if a more generic startup requirement
cannot not be implemented, the EPA should address any imposition of a
time limit for startup of a reconstructed combined cycle unit on a
case-by-case basis in recognition of the diverse combined cycle plant
designs and how such designs impact the rate at which startup can be
achieved.
As with the proposed operational standard for combined cycle
turbines, several commenters expressed support for the proposed
operational standard for simple cycle turbines during startup but
expressed concern with the amount of time provided for startup.
Commenters noted that 1 hour for a simple cycle turbine is sufficient
in most cases, however, the commenter explained that the EPA should
provide
[[Page 13534]]
additional time for extenuating circumstances including the startup of
associated post-combustion control technology which can take over an
hour to warm-up and achieve the required destruction rate. One
commenter added that initial commissioning or maintenance may require
additional startup time. The commenter suggested that the EPA allow
longer startup times and require facilities utilizing a longer startup
time to document the circumstance in their periodic report to ensure
there was a reasonable basis.
Similarly, other commenters stated that more time should be
provided for simple cycle turbines and suggested that the EPA provide 2
hours consistent with some state permits. One commenter asserted that
the federal requirements should not contradict state operating permit
conditions already in place which provide more time than the proposed
rule. Commenters stated that the final action should provide a
procedure for the EPA or state permitting authority to provide
application of an alternative standard if an operator demonstrates that
it is needed.
Response: In the final action, the definition of startup is
specified to begin at the initial combustion of fuel in the turbine.
Other operations prior to this event are not included in the time
period allocated for startup in this rule.
In response to the comments that the proposed time limit for
startup in the operational standard for startup was not sufficient, as
discussed previously in this section, the EPA reviewed continuous
emission monitoring systems (CEMS) data from 2018 for 182 turbines
subject to 40 CFR part 63, subpart YYYY. This includes both simple and
combined cycle turbines representing a range of different designs. The
analysis is documented in the memorandum titled Stationary Combustion
Turbine Startups and Shutdowns Based on Acid Rain Program CEMS Data,
which can be found in the rulemaking docket (Docket ID No. EPA-HQ-OAR-
2017-0688). As discussed in the memorandum, the stabilization of
NOX emission rates indicates stable operation (i.e., of
combustion and post-combustion controls) and was used to determine the
length of startup and shutdown periods. For simple cycle turbines, 90
percent of startups were less than 1 hour for stabilization of
emissions for all startup types (i.e., ``cold,'' ``warm,'' ``hot'';
turbine out of operation for more than 48 hours, 8-48 hours, and 0-8
hours, respectively). For combined cycle turbines, 90 percent of
``warm'' and ``hot'' startups were less than 3 hours and 72 percent of
``cold'' startups were less than 3 hours.
In a second part of the analysis, the EPA reviewed CEMS data from
2018 for turbines with oxidation catalyst. For simple cycle turbines
with oxidation catalyst, 80 percent of cold startups, 76 percent of
warm startups, and 93 percent of hot startups were less than 1 hour.
For combined cycle turbines with oxidation catalyst, at least 93
percent of startups were less than 3 hours for each startup type.
Finally, in all cases the 99-percent upper prediction limits for
startup of turbines were within the proposed time limits (at most 0.92
hours for cold starts for simple cycle turbines with oxidation catalyst
and 2.93 hours for cold starts for combined cycle turbines subject to
40 CFR part 63, subpart YYYY). Upper prediction limits were determined
for the best performing turbines in terms of startup time based on
NOX emission stabilization.
As noted in the memorandum, NOX emissions were not used
as a surrogate for HAP emissions. Rather, NOX emissions were
only used as an indicator for when stabilization of combustion and
post-combustion processes may occur. Collectively, the analyses
demonstrate that time limits in the proposed operational standards for
startup are justified. Furthermore, upper prediction limits for the
startup time to stabilization of NOX emissions were near the
startup time limits of 1 hour for simple cycle turbines and 3 hours for
combined cycle turbines, suggesting that the startup time limits are
generally neither too short nor too long with respect to emissions
stabilization.
Based on the review of CEMS data, the EPA determined that the
proposed time limits for the application of the operational standard
for startup are reasonable and consistent with what the best performers
achieve. Therefore, the EPA is not changing the proposed time limits
based on public comments. Regarding the comments that the EPA should
address time limits on a case-by-case basis, if situations occur that
warrant an alternative standard, the owner/operator can request an
alternative standard pursuant to the requirements specified in CAA
section 112(h)(3) and 40 CFR 63.6(g).
Comment: Commenters stated that the requirement within the proposed
operational standard to ``minimize the turbine's time spent at idle or
holding at low load levels'' is problematic in their opinion.
One commenter stated that greater clarity is needed between what is
termed ``startup'' and what is termed ``idle'' in the process. The
commenter explained that startup by its very nature begins at ``low
load levels'' before the turbine is safely loaded and questioned where
is the dividing line between which levels are considered startup and
which levels are considered idle, or, alternatively, at what point in
time do low load levels of startup become idle low load levels? The
commenter stated that implicit in the proposed distinction seems to be
the assumption that operators would run a turbine at ``idle'' for
unknown reasons during the startup process. The commenter asserted that
this is contrary to generally accepted operating practices. See, e.g.,
Sierra Club v. EPA, 884 F.3d 1185, 1203 (D.C. Cir. 2018) (``Boiler
operators lack incentives to combust fuel for no useful purpose, simply
as a means to avoid engaging pollution controls, so presumably they do
not tarry in heating their equipment to that point.'').
One commenter stated that the terms ``idle'' and ``holding at low
load levels'' have not been defined. The commenter asserted that
without defining these terms and how the EPA intends for units to
measure compliance with the operational standard, it is unclear what
standards combustion turbine operators need to meet outside of their
existing permit terms. The commenter stated that the proposed language
in Table 1 to 40 CFR part 63, subpart YYYY, therefore, creates
confusion as to whether these combustion turbines can continue to
operate as intended. Other commenters explained that combustion
turbines are often designed, built, permitted, and operated to be load-
following and to sometimes idle or be held at low load, when necessary,
to enable faster ramping as support for intermittent renewable
resources (e.g., solar panels). A commenter stated that some operators
may need to hold a combustion turbine at low load to allow the heat
recovery steam generator and steam turbine associated with a combined
cycle to reach normal operating temperature. According to the
commenter, the metal in the steam turbine must be warmed in a
controlled manner to allow the proper expansion of moving parts. The
commenter stated that once the heat recovery steam generator and steam
turbine metal are properly warmed and expanded, the combined cycle can,
at that time, ramp up load to meet demand. The commenter contended that
any artificial restrictions on the amount of minimum operating time
allowed may require turbine operators to risk damaging critical
equipment. The commenter added that good engineering practices require
testing at low loads following a planned maintenance outage to ensure
[[Page 13535]]
the equipment is operating safely and performing as expected. The
commenter stated that some manufacturers require this type of testing
as part of contractual agreement. Therefore, the commenter suggested
that the operational standard be revised as follows: ``During turbine
startup, you must minimize the turbine's time needed to achieve the
operating limitations provided in Table 2, taking into account the
appropriate and safe loading of the turbine and auxiliary equipment,
not to exceed 1 hour for simple cycle stationary combustion turbines
and 3 hours for combined cycle stationary combustion turbines, after
which time the operating limitation and continuous compliance
requirements in Table 2 and 5 apply.'' Another commenter provided an
example of a Prevention of Significant Deterioration permit that has
specifically authorized operation at low loads in order to provide
fast-ramping capacity to support the integration of renewable resources
(e.g., Maricopa County Air Quality Permit Department, Title V Permit
No. V95-007, ``Ocotillo PSD Permit''). The commenter noted that the
permit conditions clearly distinguish between ``startup'' and operation
at low load. The commenter also noted that the EPA's Environmental
Appeals Board reviewed and approved the Prevention of Significant
Deterioration limits in this permit.
One commenter suggested that the EPA amend the proposed language to
allow adequate time to ensure safe loading of the turbine even if it is
beyond the otherwise applicable startup time limits.
Another commenter stated that, at a minimum, the standard should
not be written to prohibit low loads, especially if the unit is
equipped with an oxidation catalyst and can meet its 4-hour average
catalyst inlet temperature operating limit during low load operation.
One commenter recommended that the EPA either eliminate the
proposed requirement, ``minimize the turbine's time spent at idle or
holding at low load levels'' or clarify the proposed language by
replacing the phrase ``time spent at idle or holding at low load
levels'' with the phrase ``operating time outside normal operations.''
Other commenters concluded that the EPA should not finalize this
requirement as part of the operational standard.
One commenter encouraged the EPA to revise the operational standard
for startup in a manner that distinguishes between continuous, stable
operation at low loads and true startup conditions.
Response: Based on these comments, the EPA is not finalizing the
proposed requirement to minimize a turbine's time spent at idle or
holding at low load levels. As stated by the commenters, some turbines
are designed and permitted to operate at idle or low load conditions.
For the final rule, there will not be an operational requirement to
minimize time spent operating in an idle or low load status. Operation
in such a status (except during startup) will be treated as normal
operation and will not have a separate standard. As discussed elsewhere
in this section, the EPA has clarified the definition for startup to
distinguish the beginning and end of the startup operational standard.
Comment: One commenter noted that 40 CFR 63.6125 states, ``If you
are operating a stationary combustion turbine that is required to
comply with the formaldehyde emission limitation and you use an
oxidation catalyst emission control device, you must monitor on a
continuous basis your catalyst inlet temperature in order to comply
with the operating limitation in Table 2 and as specified in Table 5 of
this subpart.'' The commenter then pointed out that Tables 2 and 5
refer to the calculation of a 4-hour rolling average catalyst inlet
temperature. The commenter explained that the catalyst must achieve a
certain inlet temperature before formaldehyde emissions are controlled,
so the inlet temperature monitoring should begin at the conclusion of
startup. The commenter suggested that the EPA clarify that the
calculation of the 4-hour rolling average begins at the start of the
first full clock hour after startup.
For the same reasons (i.e., turbines using an oxidation catalyst
will need time to reach the desired temperature), other commenters
suggested that the EPA clarify that the operating limitations in Table
2 do not apply during startup. These commenters also suggested that the
operating limits in Table 2 not apply during shutdown as the inlet
temperature may fall below the desired level as the combustion turbine
transitions out of operation.
One commenter also requested that the EPA clarify that the
demonstration of continuous compliance with the operating limits
specified in Table 5 do not include hours containing SSM in the
calculation. The commenter recommended that the EPA revise the
operating limitations in Table 5 of 40 CFR part 63, subpart YYYY to
include the following language, ``Any hour during which the startup
work practice standard is applicable or during which shutdown or
malfunction occurs must not be included in the calculation to
demonstrate continuous compliance with the operating limitation.''
Response: The EPA agrees with the commenter that the catalyst inlet
temperature operating limitation should not apply during startup, since
the catalyst needs time to heat up to the required temperature. The EPA
has revised the rule to reflect this change. The EPA does not agree
that the catalyst inlet temperature recorded during periods of shutdown
should not be included in the 4-hour rolling average catalyst inlet
temperature used for compliance with the catalyst inlet temperature
operating limitation. Our information is that shutdown periods are
usually brief and there is no information that the catalyst temperature
would fall below the required levels while the turbine is still
operating. Since compliance with the operating limitation is
demonstrated on a 4-hour rolling average, factoring in brief periods of
shutdown should not result in exceedances of the operating limitation.
With respect to malfunctions, the EPA is not establishing separate
emission standards for periods of malfunction and the formaldehyde
emission standards and the associated catalyst inlet temperature
monitoring requirements apply during periods of malfunction. Therefore,
we did not accept the commenter's recommendation that the catalyst
inlet temperature during a malfunction should be excluded from the
calculation of the 4-hour rolling average catalyst inlet temperature.
The EPA also notes that catalyst inlet temperatures may not be affected
by all types of malfunction. In addition, as discussed in the proposed
rule, if a source fails to comply with a requirement as a result of a
malfunction event, the EPA would determine an appropriate response and
if the EPA determines in a particular case that an enforcement action
against a source for violation of an emission standard is warranted,
the source can raise any and all defenses in that enforcement action.
Administrative and judicial procedures for addressing exceedances of
the standards fully recognize that violations may occur despite good
faith efforts to comply and can accommodate those situations. U.S.
Sugar Corp. v. EPA, 830 F.3d 579, 606-610 (2016).
4. What is the rationale for our final approach for the SSM provisions?
For the reasons explained in the proposed rule (84 FR 15046), these
amendments revise provisions related to SSM that are not consistent
with the requirement that the standards must apply at all times. We
evaluated all of the comments received on the EPA's
[[Page 13536]]
proposed amendments to the SSM provisions and made some changes to the
proposed amendments for the reasons stated above and in the Summary of
Public Comments and Responses document. We are finalizing the proposed
amendments to revise provisions related to SSM, as revised based on
public comments.
D. Electronic Reporting Requirements for the Stationary Combustion
Turbines Source Category
1. What did we propose for the Stationary Combustion Turbines source
category?
The April 12, 2019, proposal included requirements for owners and
operators of stationary combustion turbines subject to 40 CFR part 63,
subpart YYYY to submit electronic copies of required performance test
results and semiannual compliance reports through the EPA's CDX using
CEDRI. The original 2004 rule did not include any requirements for
electronic reporting.
2. How did the electronic reporting requirements change for the
Stationary Combustion Turbines source category?
The proposed amendments to require owners and operators to submit
performance test results and semiannual compliance reports through the
EPA's CDX using CEDRI are being finalized with minor corrections and
clarifications. The language at 40 CFR 63.6150(a) was amended from the
proposal to specify that the electronic report submitted semiannually
also incorporates the excess emissions and monitoring system
performance reports. The delegation of authority provision at 40 CFR
63.6170(c) was amended to specify that the EPA does not delegate the
authority to modify electronic reporting requirements to states, to
ensure that the reported information is submitted to the EPA. Table 7
of 40 CFR part 63, subpart YYYY was modified to make inapplicable the
requirements in 40 CFR 63.13 for submission of additional copies to the
EPA Regional office for electronically submitted reports.
3. What key comments did we receive on the electronic reporting
requirements, and what are our responses?
Comment: Commenters stated that the electronic reporting provisions
should clarify the electronic reporting requirements as they relate to
reports submitted to state agencies and should consider the increase in
burden if owners/operators must submit reports to both entities rather
than submitting one combined report to their delegated authority.
One commenter stated that as proposed, the owner/operator would be
required to submit one report to the EPA through the CEDRI system and
then be required to prepare a written report for state agencies such as
the Texas Commission on Environmental Quality to satisfy the regulatory
reporting obligation, thus creating a redundant reporting requirement.
The commenter requested that the final rule clarify whether the
electronic reporting requirement also applies to affected sources that
are not currently required to submit copies of reports to the EPA
because they are located in states like Texas that have received
delegation for NESHAP under 40 CFR part 63.
One commenter stated that when developing electronic reporting
provisions, the EPA should work with other regulatory authorities
(i.e., states, local agencies) to establish comparable or compatible
electronic systems. The commenter noted that companies reporting
electronically to the EPA will likely still have to submit hardcopy
reports to other agencies that do not have electronic systems, thereby
reducing or eliminating any burden savings associated with EPA
electronic reporting. In one example, based on the template structure,
an annual number for landfill gas fuel rate and heating values would be
supplied to the EPA but monthly values would still have to be supplied
to the state.
One commenter stated that if the EPA finalizes a requirement for
submission of electronic reports to CEDRI, the EPA should make
inapplicable the requirement in 40 CFR 63.13 for submission of
additional copies to the EPA Regional office. According to the
commenter, submission to CEDRI should be deemed compliance with that
requirement, because EPA Regional employees can access the reports on
CEDRI. The commenter recommended that the EPA also should include a
procedure for state agencies to similarly opt out of receiving a paper
copy.
Similarly, one commenter noted that the EPA did not add an
additional burden related to the requirement to report emissions test
data using the ERT within the Supporting Statement for the Information
Collection Request. The commenter stated that most state or local
permitting authorities will still require submittal of a paper copy of
the test report, so the ERT entry and electronic submittal to the EPA
does not replace the submittal of a test report to the local agency.
Response: To clarify the EPA's intent that electronic reporting is
required for all sources subject to the subpart, regardless of state,
local, or tribal reporting requirements, the final rule has been
amended at 63.6170(c) to add (6), that the EPA does not delegate
authority for electronic reporting requirements. The EPA is not
delegating the authority in order to ensure that the information
required to be reported is received by the EPA. The reported
information is needed for several purposes, including assessing
compliance, developing emission factors (in the case of emissions
data), and future reviews of the NESHAP. Table 7 has been revised for
the final rule to reflect that 63.13(a) is only applicable to those
reports not required to be submitted electronically.
We acknowledge that certain sources may be required to submit a
report electronically through CEDRI and a hard copy report to an air
agency that has delegation to enforce the NESHAP. The ERT is designed
to provide PDF or printed copies of reports, and these copies can be
mailed to an air agency that does not wish to use the EPA's electronic
reporting system. The burden associated with creating an emission test
report is incorporated in the cost of the emission test presented in
the Supporting Statement for the Information Collection Request (Docket
ID Item No. EPA-HQ-OAR-2017-0688-0073). This includes the development
of the test report through the ERT.
The EPA routinely discusses electronic reporting with air agencies
and EPA Regional offices. Quarterly calls are conducted with EPA
Regional offices to provide information that will be helpful in their
outreach efforts to the air agencies in their regions. The EPA has
performed demonstrations of the CEDRI reporting program and the ERT for
EPA Regional offices and their associated air agencies, as well as for
air agency groups like the Mid-Atlantic Regional Air Management
Association.
Additionally, through the E-Enterprise's Combined Air Emissions
Reporting (CAER) project, the EPA is working with air agencies to
streamline multiple emissions reporting processes. Currently, air
emissions information is collected by the EPA and air agencies through
numerous separate regulations, in a variety of formats, according to
different reporting schedules, and using multiple routes of data
transfer. The CAER project seeks to reduce the cost to industry and
government for providing and managing important environmental data.
More information on CAER can be found at: https://www.epa.gov/e-enterprise/e-enterprise-combined-air-emissions-reporting-caer.
[[Page 13537]]
4. What is the rationale for our final approach for the electronic
reporting requirements?
The EPA evaluated all of the comments on the proposed electronic
reporting requirements for this subpart. For the reasons explained in
the proposed rule and this final rule, including the document in the
docket summarizing the public comments and our responses,\7\ we are
finalizing the amendments with minor changes.
---------------------------------------------------------------------------
\7\ National Emission Standards for Hazardous Air Pollutants
from Stationary Combustion Turbines (40 CFR part 63, subpart YYYY)
Residual Risk and Technology Review, Final Amendments, Summary of
Public Comments and Responses on Proposed Rule, January 2020.
---------------------------------------------------------------------------
V. Summary of Cost, Environmental, and Economic Impacts and Additional
Analyses Conducted
A. What are the affected facilities?
The EPA has identified 777 turbines at 243 facilities that are
currently subject to the Stationary Combustion Turbines NESHAP. We are
projecting that 51 new stationary combustion turbines at 20 facilities
will become subject to the NESHAP over the next 3 years. The 51 new
turbines include 48 natural gas-fired units, one oil-fired unit, and
two landfill gas or digester gas-fired units. More information about
the number of new turbines projected over the next 3 years can be found
in the Projected Number of Turbine Units and Facilities Subject to the
Stationary Combustion Turbine National Emission Standards for Hazardous
Air (NESHAP) memorandum in the docket for this rulemaking (Docket ID
No. EPA-HQ-OAR-2017-0688).
B. What are the air quality impacts?
The baseline emissions of HAP for 777 stationary combustion
turbines at 243 facilities subject to 40 CFR part 63, subpart YYYY are
estimated to be 5,466 tpy. The HAP that is emitted in the largest
quantity is formaldehyde. The final amendments will require turbines
subject to the Stationary Combustion Turbines NESHAP to operate without
the SSM exemption. We were unable to quantify emission reductions
associated with eliminating the SSM exemption. However, eliminating the
SSM exemption will reduce emissions by requiring facilities to meet the
applicable standard during periods of SSM. We are not making any other
revisions to the emission limits, so there are no other air quality
impacts as a result of the final amendments.
C. What are the cost impacts?
Owners or operators of stationary combustion turbines that are
subject to the amendments to 40 CFR part 63, subpart YYYY, will incur
costs to review the final rule. Nationwide annual costs associated with
reviewing the final rule are estimated to be a total of $42,362 (2017
dollars) for the first year after the final rule only, or approximately
$174 (2017 dollars) per facility. We do not expect that the amendments
revising the SSM provisions and requiring electronic reporting will
impose additional burden and may result in a cost savings.
D. What are the economic impacts?
Economic impact analyses focus on changes in market prices and
output levels. If changes in market prices and output levels in the
primary markets are significant enough, impacts on other markets may
also be examined. Both the magnitude of costs needed to comply with a
proposed rule and the distribution of these costs among affected
facilities can have a role in determining how the market will change in
response to a proposed rule. The total costs associated with reviewing
the final rule are estimated to be $42,362 (2017 dollars), or $174
(2017 dollars) per facility, for the first year after the final rule.
These costs are not expected to result in a significant market impact,
regardless of whether they are passed on to the purchaser or absorbed
by the firms.
E. What are the benefits?
The EPA is not making changes to the emission limits and estimates
that the changes to the SSM requirements and requirements for
electronic reporting are not economically significant. Because these
amendments are not considered economically significant, as defined by
Executive Order 12866, and because no emission reductions were
projected, we did not estimate any benefits from reducing emissions.
F. What analysis of environmental justice did we conduct?
As discussed in the preamble to the proposed rule, to examine the
potential for any environmental justice issues that might be associated
with the source category, we performed a demographic analysis, which is
an assessment of risks to individual demographic groups of the
populations living within 5 kilometers (km) and within 50 km of the
facilities. In the analysis, we evaluated the distribution of HAP-
related cancer and noncancer risks from the Stationary Combustion
Turbines source category across different demographic groups within the
populations living near facilities. The results of this analysis
indicated that this action does not have disproportionately high and
adverse human health or environmental effects on minority populations,
low-income populations, and/or indigenous peoples. The documentation
for this decision is contained in section IV.A of the preamble to the
proposed rule and the technical report titled Risk and Technology
Review--Analysis of Demographic Factors for Populations Living Near
Stationary Combustion Turbines Source Category Operations, which is
available in the docket for this action (Docket ID No. EPA-HQ-OAR-2017-
0688).
G. What analysis of children's environmental health did we conduct?
This action's health and risk assessments are contained in sections
IV.A and B of this preamble and further documented in the risk report
titled Residual Risk Assessment for the Stationary Combustion Turbines
Source Category in Support of the 2020 Risk and Technology Review Final
Rule, which is available in the docket for this action (Docket ID No.
EPA-HQ-OAR-2017-0688).
VI. Statutory and Executive Order Reviews
Additional information about these statutes and Executive Orders
can be found at https://www.epa.gov/laws-regulations/laws-and-executive-orders.
A. Executive Orders 12866: Regulatory Planning and Review and Executive
Order 13563: Improving Regulation and Regulatory Review
This action is not a significant regulatory action and was,
therefore, not submitted to the Office of Management and Budget (OMB)
for review.
B. Executive Order 13771: Reducing Regulations and Controlling
Regulatory Costs
This action is not an Executive Order 13771 regulatory action
because this action is not significant under Executive Order 12866.
C. Paperwork Reduction Act (PRA)
This action does not impose any new information collection burden
under the PRA. OMB has previously approved the information collection
activities contained in the existing regulations and has assigned OMB
control number 2060-0540. We do not expect that the final amendments
revising the SSM provisions and requiring electronic reporting will
impose additional burden
[[Page 13538]]
not already accounted for under the existing approved burden.
D. Regulatory Flexibility Act (RFA)
I certify that this action will not have a significant economic
impact on a substantial number of small entities under the RFA. The
small entities subject to the requirements of this action are small
energy companies or governmental jurisdictions. The Agency has
determined that 10 small entities representing approximately 4 percent
of the total number of entities subject to the final rule may
experience an impact of less than 0.1 percent of revenues.
E. Unfunded Mandates Reform Act (UMRA)
This action does not contain an unfunded mandate of $100 million or
more as described in UMRA, 2 U.S.C. 1531-1538, and does not
significantly or uniquely affect small governments. The action imposes
no enforceable duty on any state, local, or tribal governments or the
private sector.
F. Executive Order 13132: Federalism
This action does not have federalism implications. It will not have
substantial direct effects on the states, on the relationship between
the national government and the states, or on the distribution of power
and responsibilities among the various levels of government.
G. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
This action does not have tribal implications as specified in
Executive Order 13175. None of the stationary combustion turbines that
have been identified as being affected by this action are owned or
operated by tribal governments or located within tribal lands. Thus,
Executive Order 13175 does not apply to this action.
H. Executive Order 13045: Protection of Children From Environmental
Health Risks and Safety Risks
This action is not subject to Executive Order 13045 because it is
not economically significant as defined in Executive Order 12866, and
because the EPA does not believe the environmental health or safety
risks addressed by this action present a disproportionate risk to
children. This action's health and risk assessments are contained in
sections III.A and B and sections IV.A and B of this preamble, and
further documented in the risk document.
I. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
This action is not subject to Executive Order 13211, because it is
not a significant regulatory action under Executive Order 12866.
J. National Technology Transfer and Advancement Act (NTTAA) and 1 CFR
Part 51
This action involves technical standards. The EPA has decided to
use ANSI/ASME PTC 19.10-1981 Part 10 (1981), ``Flue and Exhaust Gas
Analyses'' (the manual portion only) as an alternative to EPA Method 3B
and to incorporate the alternative method by reference. The ANSI/ASME
PTC 19.10-1981 Part 10 (1981) method incorporates both manual and
instrumental methodologies for the determination of O2
content. The manual method segment of the O2 determination
is performed through the absorption of O2. The method is
reasonably available from the American Society of Mechanical Engineers
at https://www.asme.org; by mail at Three Park Avenue, New York, NY
10016-5990; or by telephone at (800) 843-2763. The EPA has decided to
use ASTM D6522-11, ``Standard Test Method for the Determination of
Nitrogen Oxides, Carbon Monoxide, and Oxygen Concentrations in
Emissions from Natural Gas-Fired Reciprocating Engines, Combustion
Turbines, Boilers and Process Heaters Using Portable Analyzers'' as an
alternative to EPA Method 3A for turbines fueled by natural gas and to
incorporate the alternative method by reference. The ASTM D6522-11
method is an electrochemical cell based portable analyzer method which
may be used for the determination of NOX, CO, and
O2 in emission streams form stationary sources. Also,
instead of the current ASTM D6348-12e1 standard (``Determination of
Gaseous Compounds by Extractive Direct Interface Fourier Transform
Infrared (FTIR) Spectroscopy''), the Stationary Combustion Turbines
NESHAP currently references ASTM D6348-03 as an alternative to EPA
Method 320. We are updating the NESHAP to reference the most current
version of the ASTM D6348 method as an alternative to EPA Method 320.
When using this method, the test plan preparation and implementation
requirements in Annexes A1 through A8 to ASTM D6348-12e1 are mandatory.
The ASTM D6348-12e1 method is an extractive FTIR spectroscopy-based
field test method and is used to quantify gas phase concentrations of
multiple target compounds in emission streams from stationary sources.
The ASTM standards are reasonably available from the American Society
for Testing and Materials, 100 Barr Harbor Drive, Post Office Box C700,
West Conshohocken, PA 19428-2959. See https://www.astm.org/.
The EPA identified an additional seven voluntary consensus
standards (VCS) as being potentially applicable to this rule. After
reviewing the available standards, the EPA determined that the seven
VCS would not be practical due to lack of equivalency, documentation,
validation data, and/or other important technical and policy
considerations. For further information, see the memorandum titled
Voluntary Consensus Standard Results for National Emission Standards
for Hazardous Air Pollutants: Stationary Combustion Turbines Risk and
Technology, in the docket for this rule (Docket ID No. EPA-HQ-OAR-2017-
0688).
K. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
The EPA believes that this action does not have disproportionately
high and adverse human health or environmental effects on minority
populations, low-income populations, and/or indigenous peoples, as
specified in Executive Order 12898 (59 FR 7629, February 16, 1994).
The documentation for this decision is contained in section IV.A of
this preamble and the technical report, Risk and Technology Review
Analysis of Demographic Factors for Populations Living Near Stationary
Combustion Turbines Source Category Operations.
L. Congressional Review Act (CRA)
This action is subject to the CRA, and the EPA will submit a rule
report to each House of the Congress and to the Comptroller General of
the United States. This action is not a ``major rule'' as defined by 5
U.S.C. 804(2).
List of Subjects in 40 CFR Part 63
Environmental protection, Administrative practice and procedures,
Air pollution control, Hazardous substances, Incorporation by
reference, Intergovernmental relations, Reporting and recordkeeping
requirements.
Dated: January 31, 2020.
Andrew R. Wheeler,
Administrator.
For the reasons set forth in the preamble, the EPA amends 40 CFR
part 63 as follows:
[[Page 13539]]
PART 63--NATIONAL EMISSION STANDARDS FOR HAZARDOUS AIR POLLUTANTS
FOR SOURCE CATEGORIES
0
1. The authority citation for part 63 continues to read as follows:
Authority: 42 U.S.C. 7401 et seq.
Subpart A--General Provisions
0
2. Section 63.14 is amended by revising paragraphs (e)(1) and (h)(85),
redesignating paragraphs (h)(94) through (111) as (h)(95) through
(112), and adding new paragraph (h)(94) to read as follows.
Sec. 63.14 Incorporations by reference.
* * * * *
(e) * * *
(1) ANSI/ASME PTC 19.10-1981, Flue and Exhaust Gas Analyses [Part
10, Instruments and Apparatus], issued August 31, 1981, IBR approved
for Sec. Sec. 63.309(k), 63.457(k), 63.772(e) and (h), 63.865(b),
63.1282(d) and (g), 63.1625(b), 63.3166(a), 63.3360(e), 63.3545(a),
63.3555(a), 63.4166(a), 63.4362(a), 63.4766(a), 63.4965(a), 63.5160(d),
table 4 to subpart UUUU, table 3 to subpart YYYY, 63.9307(c),
63.9323(a), 63.11148(e), 63.11155(e), 63.11162(f), 63.11163(g),
63.11410(j), 63.11551(a), 63.11646(a), and 63.11945, table 5 to subpart
DDDDD, table 4 to subpart JJJJJ, table 4 to subpart KKKKK, tables 4 and
5 to subpart UUUUU, table 1 to subpart ZZZZZ, and table 4 to subpart
JJJJJJ.
* * * * *
(h) * * *
(85) ASTM D6348-12e1, Standard Test Method for Determination of
Gaseous Compounds by Extractive Direct Interface Fourier Transform
Infrared (FTIR) Spectroscopy, Approved February 1, 2012, IBR approved
for Sec. 63.1571(a) and table 3 to subpart YYYY.
* * * * *
(94) ASTM D6522-11, Standard Test Method for Determination of
Nitrogen Oxides, Carbon Monoxide, and Oxygen Concentrations in
Emissions from Natural Gas-Fired Reciprocating Engines, Combustion
Turbines, Boilers, and Process Heaters Using Portable Analyzers,
Approved December 1, 2011, IBR approved for table 3 to subpart YYYY.
* * * * *
Subpart YYYY--National Emission Standards for Hazardous Air
Pollutants for Stationary Combustion Turbines
0
3. Revise Sec. 63.6105 to read as follows:
Sec. 63.6105 What are my general requirements for complying with
this subpart?
(a) Before September 8, 2020, you must be in compliance with the
emission limitations and operating limitations which apply to you at
all times except during startup, shutdown, and malfunctions. After
September 8, 2020, you must be in compliance with the emission
limitations, operating limitations, and other requirements in this
subpart which apply to you at all times.
(b) Before September 8, 2020, if you must comply with emission and
operating limitations, you must operate and maintain your stationary
combustion turbine, oxidation catalyst emission control device or other
air pollution control equipment, and monitoring equipment in a manner
consistent with good air pollution control practices for minimizing
emissions at all times including during startup, shutdown, and
malfunction.
(c) After September 8, 2020, at all times, the owner or operator
must operate and maintain any affected source, including associated air
pollution control equipment and monitoring equipment, in a manner
consistent with safety and good air pollution control practices for
minimizing emissions. The general duty to minimize emissions does not
require the owner or operator to make any further efforts to reduce
emissions if levels required by the applicable standard have been
achieved. Determination of whether a source is operating in compliance
with operation and maintenance requirements will be based on
information available to the Administrator which may include, but is
not limited to, monitoring results, review of operation and maintenance
procedures, review of operation and maintenance records, and inspection
of the source.
0
4. Section 63.6120 is amended by revising paragraphs (b) and (c) to
read as follows:
Sec. 63.6120 What performance tests and other procedures must I use?
* * * * *
(b) Each performance test must be conducted according to the
requirements in Table 3 of this subpart. Before September 8, 2020, each
performance test must be conducted according to the requirements of the
General Provisions at Sec. 63.7(e)(1).
(c) Performance tests must be conducted at high load, defined as
100 percent plus or minus 10 percent. Before September 8, 2020, do not
conduct performance tests or compliance evaluations during periods of
startup, shutdown, or malfunction. After September 8, 2020, performance
tests shall be conducted under such conditions based on representative
performance of the affected source for the period being tested.
Representative conditions exclude periods of startup and shutdown. The
owner or operator may not conduct performance tests during periods of
malfunction. The owner or operator must record the process information
that is necessary to document operating conditions during the test and
include in such record an explanation to support that such conditions
represent normal operation. Upon request, the owner or operator shall
make available to the Administrator such records as may be necessary to
determine the conditions of performance tests.
* * * * *
0
5. Section 63.6125 is amended by adding paragraph (e) to read as
follows:
Sec. 63.6125 What are my monitor installation, operation, and
maintenance requirements?
* * * * *
(e) After September 8, 2020, if you are required to use a
continuous monitoring system (CMS), you must develop and implement a
CMS quality control program that included written procedures for CMS
according to Sec. 63.8(d)(1) through (2). You must keep these written
procedures on record for the life of the affected source or until the
affected source is no longer subject to the provisions of this part, to
be made available for inspection, upon request, by the Administrator.
If the performance evaluation plan is revised, the owner or operator
shall keep previous (i.e., superseded) versions of the performance
evaluation plan on record to be made available for inspection, upon
request, by the Administrator, for a period of 5 years after each
revision to the plan. The program of corrective action should be
included in the plan required under Sec. 63.8(d)(2).
0
6. Section 63.6140 is amended by revising paragraph (c) to read as
follows:
Sec. 63.6140 How do I demonstrate continuous compliance with the
emission and operating limitations?
* * * * *
(c) Before September 8, 2020, consistent with Sec. Sec. 63.6(e)
and 63.7(e)(1), deviations that occur during a period of startup,
shutdown, and malfunction are not violations if you have operated your
stationary combustion turbine in accordance with Sec. 63.6(e)(1)(i).
0
7. Section 63.6150 is amended by:
[[Page 13540]]
0
a. Revising paragraph (a) introductory text, paragraph (a)(4)
introductory text, paragraph (c) introductory text, and paragraph (e)
introductory text, and
0
b. Adding paragraphs (a)(5), (f), (g), (h) and (i).
The revisions and additions read as follows:
Sec. 63.6150 What reports must I submit and when?
(a) Compliance report. Anyone who owns or operates a stationary
combustion turbine which must meet the emission limitation for
formaldehyde must submit a semiannual compliance report according to
Table 6 of this subpart. The semiannual compliance report must contain
the information described in paragraphs (a)(1) through (5) of this
section. The semiannual compliance report, including the excess
emissions and monitoring system performance reports of Sec.
63.10(e)(3), must be submitted by the dates specified in paragraphs
(b)(1) through (5) of this section, unless the Administrator has
approved a different schedule. After September 8, 2020, or once the
reporting template has been available on the Compliance and Emissions
Data Reporting Interface (CEDRI) website for 180 days, whichever date
is later, you must submit all subsequent reports to the EPA following
the procedure specified in paragraph (g) of this section.
* * * * *
(4) Before September 8, 2020, for each deviation from an emission
limitation, the compliance report must contain the information in
paragraphs (a)(4)(i) through (iii) of this section.
* * * * *
(5) After September 8, 2020, report each deviation in the
semiannual compliance report. Report the information specified in
paragraphs (a)(5)(i) through (iv) of this section.
(i) Report the number of deviations. For each instance, report the
start date, start time, duration, and cause of each deviation, and the
corrective action taken.
(ii) For each deviation, the report must include a list of the
affected sources or equipment, an estimate of the quantity of each
regulated pollutant emitted over any emission limit, a description of
the method used to estimate the emissions.
(iii) Information on the number, duration, and cause for monitor
downtime incidents (including unknown cause, if applicable, other than
downtime associated with zero and span and other daily calibration
checks), as applicable, and the corrective action taken.
(iv) Report the total operating time of the affected source during
the reporting period.
* * * * *
(c) If you are operating as a stationary combustion turbine which
fires landfill gas or digester gas equivalent to 10 percent or more of
the gross heat input on an annual basis, or a stationary combustion
turbine where gasified MSW is used to generate 10 percent or more of
the gross heat input on an annual basis, you must submit an annual
report according to Table 6 of this subpart by the date specified
unless the Administrator has approved a different schedule, according
to the information described in paragraphs (d)(1) through (5) of this
section. You must report the data specified in (c)(1) through (3) of
this section. After September 8, 2020, you must submit all subsequent
reports to the EPA following the procedure specified in paragraph (g)
of this section.
* * * * *
(e) If you are operating a lean premix gas-fired stationary
combustion turbine or a diffusion flame gas-fired stationary combustion
turbine as defined by this subpart, and you use any quantity of
distillate oil to fire any new or existing stationary combustion
turbine which is located at the same major source, you must submit an
annual report according to Table 6 of this subpart by the date
specified unless the Administrator has approved a different schedule,
according to the information described in paragraphs (d)(1) through (5)
of this section. You must report the data specified in (e)(1) through
(3) of this section. After September 8, 2020, you must submit all
subsequent reports to the EPA following the procedure specified in
paragraph (g) of this section.
* * * * *
(f) Performance test report. After September 8, 2020, within 60
days after the date of completing each performance test required by
this subpart, you must submit the results of the performance test (as
specified in Sec. 63.6145(f)) following the procedures specified in
paragraphs (f)(1) through (3) of this section.
(1) Data collected using test methods supported by the EPA's
Electronic Reporting Tool (ERT) as listed on the EPA's ERT website
(https://www.epa.gov/electronic-reporting-air-emissions/electronic-reporting-tool-ert) at the time of the test. Submit the results of the
performance test to the EPA via the CEDRI, which can be accessed
through the EPA's Central Data Exchange (CDX) (https://cdx.epa.gov/).
The data must be submitted in a file format generated through the use
of the EPA's ERT. Alternatively, you may submit an electronic file
consistent with the extensible markup language (XML) schema listed on
the EPA's ERT website.
(2) Data collected using test methods that are not supported by the
EPA's ERT as listed on the EPA's ERT website at the time of the test.
The results of the performance test must be included as an attachment
in the ERT or an alternate electronic file consistent with the XML
schema listed on the EPA's ERT website. Submit the ERT generated
package or alternative file to the EPA via CEDRI.
(3) Confidential business information (CBI). If you claim some of
the information submitted under paragraph (f)(1) of this section is
CBI, you must submit a complete file, including information claimed to
be CBI, to the EPA. The file must be generated through the use of the
EPA's ERT or an alternate electronic file consistent with the XML
schema listed on the EPA's ERT website. Submit the file on a compact
disc, flash drive, or other commonly used electronic storage medium and
clearly mark the medium as CBI. Mail the electronic medium to U.S. EPA/
OAQPS/CORE CBI Office, Attention: Group Leader, Measurement Policy
Group, MD C404-02, 4930 Old Page Rd., Durham, NC 27703. The same file
with the CBI omitted must be submitted to the EPA via the EPA's CDX as
described in paragraph (f)(1) of this section.
(g) If you are required to submit reports following the procedure
specified in this paragraph, you must submit reports to the EPA via
CEDRI, which can be accessed through the EPA's CDX (https://cdx.epa.gov/). You must use the appropriate electronic report template
on the CEDRI website (https://www.epa.gov/electronic-reporting-air-emissions/compliance-and-emissions-data-reporting-interface-cedri) for
this subpart. The date report templates become available will be listed
on the CEDRI website. The report must be submitted by the deadline
specified in this subpart, regardless of the method in which the report
is submitted. If you claim some of the information required to be
submitted via CEDRI is CBI, submit a complete report, including
information claimed to be CBI, to the EPA. The report must be generated
using the appropriate form on the CEDRI website. Submit the file on a
compact disc, flash drive, or other commonly used electronic storage
medium and clearly mark the medium
[[Page 13541]]
as CBI. Mail the electronic medium to U.S. EPA/OAQPS/CORE CBI Office,
Attention: Group Leader, Measurement Policy Group, MD C404-02, 4930 Old
Page Rd., Durham, NC 27703. The same file with the CBI omitted must be
submitted to the EPA via the EPA's CDX as described earlier in this
paragraph.
(h) If you are required to electronically submit a report through
CEDRI in the EPA's CDX, you may assert a claim of EPA system outage for
failure to timely comply with the reporting requirement. To assert a
claim of EPA system outage, you must meet the requirements outlined in
paragraphs (h)(1) through (7) of this section.
(1) You must have been or will be precluded from accessing CEDRI
and submitting a required report within the time prescribed due to an
outage of either the EPA's CEDRI or CDX systems.
(2) The outage must have occurred within the period of time
beginning five business days prior to the date that the submission is
due.
(3) The outage may be planned or unplanned.
(4) You must submit notification to the Administrator in writing as
soon as possible following the date you first knew, or through due
diligence should have known, that the event may cause or has caused a
delay in reporting.
(5) You must provide to the Administrator a written description
identifying:
(i) The date(s) and time(s) when CDX or CEDRI was accessed and the
system was unavailable;
(ii) A rationale for attributing the delay in reporting beyond the
regulatory deadline to EPA system outage;
(iii) Measures taken or to be taken to minimize the delay in
reporting; and
(iv) The date by which you propose to report, or if you have
already met the reporting requirement at the time of the notification,
the date you reported.
(6) The decision to accept the claim of EPA system outage and allow
an extension to the reporting deadline is solely within the discretion
of the Administrator.
(7) In any circumstance, the report must be submitted
electronically as soon as possible after the outage is resolved.
(i) If you are required to electronically submit a report through
CEDRI in the EPA's CDX, you may assert a claim of force majeure for
failure to timely comply with the reporting requirement. To assert a
claim of force majeure, you must meet the requirements outlined in
paragraphs (i)(1) through (5) of this section.
(1) You may submit a claim if a force majeure event is about to
occur, occurs, or has occurred or there are lingering effects from such
an event within the period of time beginning five business days prior
to the date the submission is due. For the purposes of this section, a
force majeure event is defined as an event that will be or has been
caused by circumstances beyond the control of the affected facility,
its contractors, or any entity controlled by the affected facility that
prevents you from complying with the requirement to submit a report
electronically within the time period prescribed. Examples of such
events are acts of nature (e.g., hurricanes, earthquakes, or floods),
acts of war or terrorism, or equipment failure or safety hazard beyond
the control of the affected facility (e.g., large scale power outage).
(2) You must submit notification to the Administrator in writing as
soon as possible following the date you first knew, or through due
diligence should have known, that the event may cause or has caused a
delay in reporting.
(3) You must provide to the Administrator:
(i) A written description of the force majeure event;
(ii) A rationale for attributing the delay in reporting beyond the
regulatory deadline to the force majeure event;
(iii) Measures taken or to be taken to minimize the delay in
reporting; and
(iv) The date by which you propose to report, or if you have
already met the reporting requirement at the time of the notification,
the date you reported.
(4) The decision to accept the claim of force majeure and allow an
extension to the reporting deadline is solely within the discretion of
the Administrator.
(5) In any circumstance, the reporting must occur as soon as
possible after the force majeure event occurs.
0
8. Section 63.6155 is amended by revising paragraph (a) introductory
text and paragraphs (a)(3) through (5) and adding paragraphs (a)(6),
(a)(7), and (d) to read as follows:
Sec. 63.6155 What records must I keep?
(a) You must keep the records as described in paragraphs (a)(1)
through (7) of this section.
* * * * *
(3) Before September 8, 2020, records of the occurrence and
duration of each startup, shutdown, or malfunction as required in Sec.
63.10(b)(2)(i).
(4) Before September 8, 2020, records of the occurrence and
duration of each malfunction of the air pollution control equipment, if
applicable, as required in Sec. 63.10(b)(2)(ii).
(5) Records of all maintenance on the air pollution control
equipment as required in Sec. 63.10(b)(2)(iii).
(6) After September 8, 2020, records of the date, time, and
duration of each startup period, recording the periods when the
affected source was subject to the standard applicable to startup.
(7) After September 8, 2020, keep records as follows.
(i) Record the number of deviations. For each deviation, record the
date, time, cause, and duration of the deviation.
(ii) For each deviation, record and retain a list of the affected
sources or equipment, an estimate of the quantity of each regulated
pollutant emitted over any emission limit and a description of the
method used to estimate the emissions.
(iii) Record actions taken to minimize emissions in accordance with
Sec. 63.6105(c), and any corrective actions taken to return the
affected unit to its normal or usual manner of operation.
* * * * *
(d) Any records required to be maintained by this part that are
submitted electronically via the EPA's CEDRI may be maintained in
electronic format. This ability to maintain electronic copies does not
affect the requirement for facilities to make records, data, and
reports available upon request to a delegated air agency or the EPA as
part of an on-site compliance evaluation.
0
9. Section 63.6170 is amended by adding paragraph (c)(6) to read as
follows:
Sec. 63.6170 Who implements and enforces this subpart?
* * * * *
(c) * * *
(6) Approval of an alternative to any electronic reporting to the
EPA required by this subpart.
* * * * *
0
10. Section 63.6175 is amended by revising the definition for
``Deviation'' and adding a definition for ``Startup'' to read as
follows:
Sec. 63.6175 What definitions apply to this subpart?
* * * * *
Deviation means any instance in which an affected source subject to
this subpart, or an owner or operator of such a source:
(1) Fails to meet any requirement or obligation established by this
subpart, including but not limited to any emission limitation or
operating limitation;
(2) Fails to meet any term or condition that is adopted to
implement an
[[Page 13542]]
applicable requirement in this subpart and that is included in the
operating permit for any affected source required to obtain such a
permit;
(3) Fails to meet any emission limitation or operating limitation
in this subpart during malfunction, regardless of whether or not such
failure is permitted by this subpart;
(4) Before September 8, 2020, fails to satisfy the general duty to
minimize emissions established by Sec. 63.6(e)(1)(i), or
(5) After September 8, 2020, fails to satisfy the general duty to
minimize emissions established by Sec. 63.6105.
* * * * *
Startup begins at the first firing of fuel in the stationary
combustion turbine. For simple cycle turbines, startup ends when the
stationary combustion turbine has reached stable operation or after 1
hour, whichever is less. For combined cycle turbines, startup ends when
the stationary combustion turbine has reached stable operation or after
3 hours, whichever is less. Turbines in combined cycle configurations
that are operating as simple cycle turbines must meet the startup
requirements for simple cycle turbines while operating as simple cycle
turbines.
* * * * *
0
11. Table 1 to Subpart YYYY of Part 63 is revised to read as follows:
Table 1 to Subpart YYYY of Part 63--Emission Limitations
As stated in Sec. 63.6100, you must comply with the following
emission limitations.
------------------------------------------------------------------------
For each new or reconstructed
stationary combustion turbine You must meet the following
described in Sec. 63.6100 which emission limitations . . .
is . . .
------------------------------------------------------------------------
1. a lean premix gas-fired limit the concentration of
stationary combustion turbine as formaldehyde to 91 ppbvd or less
defined in this subpart, at 15-percent O2, except during
2. a lean premix oil-fired turbine startup. The period of
stationary combustion turbine as time for turbine startup is
defined in this subpart, subject to the limits specified in
3. a diffusion flame gas-fired the definition of startup in Sec.
stationary combustion turbine as 63.6175.
defined in this subpart, or
4. a diffusion flame oil-fired
stationary combustion turbine as
defined in this subpart.
------------------------------------------------------------------------
0
12. Table 2 to Subpart YYYY of Part 63 is revised to read as follows:
Table 2 to Subpart YYYY of Part 63--Operating Limitations
As stated in Sec. Sec. 63.6100 and 63.6140, you must comply with
the following operating limitations.
------------------------------------------------------------------------
For . . . You must . . .
------------------------------------------------------------------------
1. each stationary combustion turbine maintain the 4-hour rolling
that is required to comply with the average of the catalyst inlet
emission limitation for formaldehyde temperature within the range
and is using an oxidation catalyst. suggested by the catalyst
manufacturer. You are not
required to use the catalyst
inlet temperature data that is
recorded during engine startup
in the calculations of the 4-
hour rolling average catalyst
inlet temperature.
2. each stationary combustion turbine maintain any operating
that is required to comply with the limitations approved by the
emission limitation for formaldehyde Administrator.
and is not using an oxidation catalyst.
------------------------------------------------------------------------
0
13. Table 3 to Subpart YYYY of Part 63 is revised to read as follows:
Table 3 to Subpart YYYY of Part 63--Requirements for Performance Tests
and Initial Compliance Demonstrations
As stated in Sec. 63.6120, you must comply with the following
requirements for performance tests and initial compliance
demonstrations.
------------------------------------------------------------------------
According to the
You must . . . Using . . . following
requirements . . .
------------------------------------------------------------------------
a. demonstrate formaldehyde Test Method 320 of formaldehyde
emissions meet the emission 40 CFR part 63, concentration must
limitations specified in appendix A; ASTM be corrected to 15-
Table 1 by a performance D6348-12e1 \1\ percent O2, dry
test initially and on an provided that the basis. Results of
annual basis AND. test plan this test consist
preparation and of the average of
implementation the three 1-hour
provisions of runs. Test must be
Annexes A1 through conducted within 10
A8 are followed and percent of 100-
the %R as percent load.
determined in Annex
A5 is equal or
greater than 70%
and less than or
equal to 130%; \2\
or other methods
approved by the
Administrator.
b. select the sampling port Method 1 or 1A of 40 if using an air
location and the number of CFR part 60, pollution control
traverse points AND. appendix A. device, the
sampling site must
be located at the
outlet of the air
pollution control
device.
c. determine the O2 Method 3A or 3B of measurements to
concentration at the 40 CFR part 60, determine O2
sampling port location AND. appendix A; ANSI/ concentration must
ASME PTC 19.10-1981 be made at the same
\1\ (Part 10) time as the
manual portion performance test.
only; ASTM D6522-11
\1\ if the turbine
is fueled by
natural gas.
[[Page 13543]]
d. determine the moisture Method 4 of 40 CFR measurements to
content at the sampling part 60, appendix A determine moisture
port location for the or Test Method 320 content must be
purposes of correcting the of 40 CFR part 63, made at the same
formaldehyde concentration appendix A, or ASTM time as the
to a dry basis. D6348-12e1 \1\. performance test.
------------------------------------------------------------------------
\1\ Incorporated by reference, see Sec. 63.14.
\2\ The %R value for each compound must be reported in the test report,
and all field measurements must be corrected with the calculated %R
value for that compound using the following equation:
Reported Results = ((Measured Concentration in Stack)/(%R)) x 100.
0
14. Table 7 to Subpart YYYY of Part 63 is revised to read as follows:
Table 7 to Subpart YYYY of Part 63--Applicability of General Provisions
to Subpart YYYY
You must comply with the applicable General Provisions
requirements:
----------------------------------------------------------------------------------------------------------------
Citation Subject Applies to subpart YYYY Explanation
----------------------------------------------------------------------------------------------------------------
Sec. 63.1.................. General applicability of Yes.......................... Additional terms defined
the General Provisions. in Sec. 63.6175.
Sec. 63.2.................. Definitions............. Yes.......................... Additional terms defined
in Sec. 63.6175.
Sec. 63.3.................. Units and abbreviations. Yes..........................
Sec. 63.4.................. Prohibited activities... Yes..........................
Sec. 63.5.................. Construction and Yes..........................
reconstruction.
Sec. 63.6(a)............... Applicability........... Yes..........................
Sec. 63.6(b)(1)-(4)........ Compliance dates for new Yes..........................
and reconstructed
sources.
Sec. 63.6(b)(5)............ Notification............ Yes..........................
Sec. 63.6(b)(6)............ [Reserved]..............
Sec. 63.6(b)(7)............ Compliance dates for new Yes..........................
and reconstructed area
sources that become
major.
Sec. 63.6(c)(1)-(2)........ Compliance dates for Yes..........................
existing sources.
Sec. 63.6(c)(3)-(4)........ [Reserved]..............
Sec. 63.6(c)(5)............ Compliance dates for Yes..........................
existing area sources
that become major.
Sec. 63.6(d)............... [Reserved]..............
Sec. 63.6(e)(1)(i)......... General duty to minimize Yes before September 8, 2020.
emissions. No after September 8, 2020.
See Sec. 63.6105 for
general duty requirement..
Sec. 63.6(e)(1)(ii)........ Requirement to correct Yes before September 8, 2020.
malfunctions ASAP. No after September 8, 2020...
Sec. 63.6(e)(1)(iii)....... Operation and Yes..........................
Maintenance
Requirements.
Sec. 63.6(e)(2)............ [Reserved]..............
Sec. 63.6(e)(3)............ SSMP.................... Yes before September 8, 2020.
No after September 8, 2020...
Sec. 63.6(f)(1)............ Applicability of Yes before September 8, 2020.
standards except during No after September 8, 2020...
startup, shutdown, or
malfunction (SSM).
Sec. 63.6(f)(2)............ Methods for determining Yes..........................
compliance.
Sec. 63.6(f)(3)............ Finding of compliance... Yes..........................
Sec. 63.6(g)(1)-(3)........ Use of alternative Yes..........................
standard.
Sec. 63.6(h)............... Opacity and visible No........................... Subpart YYYY does not
emission standards. contain opacity or
visible emission
standards.
Sec. 63.6(i)............... Compliance extension Yes..........................
procedures and criteria.
Sec. 63.6(j)............... Presidential compliance Yes..........................
exemption.
Sec. 63.7(a)(1)-(2)........ Performance test dates.. Yes.......................... Subpart YYYY contains
performance test dates
at Sec. 63.6110.
Sec. 63.7(a)(3)............ Section 114 authority... Yes..........................
Sec. 63.7(b)(1)............ Notification of Yes..........................
performance test.
Sec. 63.7(b)(2)............ Notification of Yes..........................
rescheduling.
[[Page 13544]]
Sec. 63.7(c)............... Quality assurance/test Yes..........................
plan.
Sec. 63.7(d)............... Testing facilities...... Yes..........................
Sec. 63.7(e)(1)............ Conditions for Yes before September 8, 2020.
conducting performance No after September 8, 2020...
tests.
Sec. 63.7(e)(2)............ Conduct of performance Yes.......................... Subpart YYYY specifies
tests and reduction of test methods at Sec.
data. 63.6120.
Sec. 63.7(e)(3)............ Test run duration....... Yes..........................
Sec. 63.7(e)(4)............ Administrator may Yes..........................
require other testing
under section 114 of
the CAA.
Sec. 63.7(f)............... Alternative test method Yes..........................
provisions.
Sec. 63.7(g)............... Performance test data Yes..........................
analysis,
recordkeeping, and
reporting.
Sec. 63.7(h)............... Waiver of tests......... Yes..........................
Sec. 63.8(a)(1)............ Applicability of Yes.......................... Subpart YYYY contains
monitoring requirements. specific requirements
for monitoring at Sec.
63.6125.
Sec. 63.8(a)(2)............ Performance Yes..........................
specifications.
Sec. 63.8(a)(3)............ [Reserved]..............
Sec. 63.8(a)(4)............ Monitoring for control No...........................
devices.
Sec. 63.8(b)(1)............ Monitoring.............. Yes..........................
Sec. 63.8(b)(2)-(3)........ Multiple effluents and Yes..........................
multiple monitoring
systems.
Sec. 63.8(c)(1)............ Monitoring system Yes..........................
operation and
maintenance.
Sec. 63.8(c)(1)(i)......... General duty to minimize Yes before September 8, 2020.
emissions and CMS No after September 8, 2020...
operation.
Sec. 63.8(c)(1)(ii)........ Parts for repair of CMS Yes..........................
readily available.
Sec. 63.8(c)(1)(iii)....... Requirement to develop Yes before September 8, 2020.
SSM Plan for CMS. No after September 8, 2020...
Sec. 63.8(c)(2)-(3)........ Monitoring system Yes..........................
installation.
Sec. 63.8(c)(4)............ Continuous monitoring Yes.......................... Except that subpart YYYY
system (CMS) does not require
requirements. continuous opacity
monitoring systems
(COMS).
Sec. 63.8(c)(5)............ COMS minimum procedures. No...........................
Sec. 63.8(c)(6)-(8)........ CMS requirements........ Yes.......................... Except that subpart YYYY
does not require COMS.
Sec. 63.8(d)(1)-(2)........ CMS quality control..... Yes..........................
Sec. 63.8(d)(3)............ Written procedures for Yes before September 8, 2020.
CMS. No after September 8, 2020...
Sec. 63.8(e)............... CMS performance Yes.......................... Except for Sec.
evaluation. 63.8(e)(5)(ii), which
applies to COMS.
Sec. 63.8(f)(1)-(5)........ Alternative monitoring Yes..........................
method.
Sec. 63.8(f)(6)............ Alternative to relative Yes..........................
accuracy test.
Sec. 63.8(g)............... Data reduction.......... Yes.......................... Except that provisions
for COMS are not
applicable. Averaging
periods for
demonstrating
compliance are
specified at Sec. Sec.
63.6135 and 63.6140.
Sec. 63.9(a)............... Applicability and State Yes..........................
delegation of
notification
requirements.
Sec. 63.9(b)(1)-(5)........ Initial notifications... Yes.......................... Except that Sec.
63.9(b)(3) is reserved.
Sec. 63.9(c)............... Request for compliance Yes..........................
extension.
Sec. 63.9(d)............... Notification of special Yes..........................
compliance requirements
for new sources.
Sec. 63.9(e)............... Notification of Yes..........................
performance test.
Sec. 63.9(f)............... Notification of visible No........................... Subpart YYYY does not
emissions/opacity test. contain opacity or VE
standards.
Sec. 63.9(g)(1)............ Notification of Yes..........................
performance evaluation.
[[Page 13545]]
Sec. 63.9(g)(2)............ Notification of use of No........................... Subpart YYYY does not
COMS data. contain opacity or VE
standards.
Sec. 63.9(g)(3)............ Notification that Yes..........................
criterion for
alternative to relative
accuracy test audit
(RATA) is exceeded.
Sec. 63.9(h)............... Notification of Yes.......................... Except that
compliance status. notifications for
sources not conducting
performance tests are
due 30 days after
completion of
performance
evaluations. Sec.
63.9(h)(4) is reserved.
Sec. 63.9(i)............... Adjustment of submittal Yes..........................
deadlines.
Sec. 63.9(j)............... Change in previous Yes..........................
information.
Sec. 63.10(a).............. Administrative Yes..........................
provisions for
recordkeeping and
reporting.
Sec. 63.10(b)(1)........... Record retention........ Yes..........................
Sec. 63.10(b)(2)(i)........ Recordkeeping of Yes before September 8, 2020.
occurrence and duration No after September 8, 2020...
of startups and
shutdowns.
Sec. 63.10(b)(2)(ii)....... Recordkeeping of Yes before September 8, 2020.
failures to meet a No after September 8, 2020.
standard. See Sec. 63.6155 for
recordkeeping of (1) date,
time and duration; (2)
listing of affected source
or equipment, and an
estimate of the quantity of
each regulated pollutant
emitted over the standard;
and (3) actions to minimize
emissions and correct the
failure..
Sec. 63.10(b)(2)(iii)...... Maintenance records..... Yes..........................
Sec. 63.10(b)(2)(iv)-(v)... Records related to Yes before September 8, 2020.
actions during SSM. No after September 8, 2020...
Sec. 63.10(b)(2)(vi)-(xi).. CMS records............. Yes..........................
Sec. 63.10(b)(2)(xii)...... Record when under waiver Yes..........................
Sec. 63.10(b)(2)(xiii)..... Records when using Yes..........................
alternative to RATA.
Sec. 63.10(b)(2)(xiv)...... Records of supporting Yes..........................
documentation.
Sec. 63.10(b)(3)........... Records of applicability Yes..........................
determination.
Sec. 63.10(c)(1)-(14)...... Additional records for Yes.......................... Except that Sec.
sources using CMS. 63.10(c)(2)-(4) and (9)
are reserved.
Sec. 63.10(c)(15).......... Use of SSM Plan......... Yes before September 8, 2020.
No after September 8, 2020...
Sec. 63.10(d)(1)........... General reporting Yes..........................
requirements.
Sec. 63.10(d)(2)........... Report of performance Yes..........................
test results.
Sec. 63.10(d)(3)........... Reporting opacity or VE No........................... Subpart YYYY does not
observations. contain opacity or VE
standards.
Sec. 63.10(d)(4)........... Progress reports........ Yes..........................
Sec. 63.10(d)(5)........... Startup, shutdown, and No. After September 8, 2020,
malfunction reports. see 63.6150(a) for
malfunction reporting
requirements.
Sec. 63.10(e)(1) and (2)(i) Additional CMS reports.. Yes..........................
Sec. 63.10(e)(2)(ii)....... COMS-related report..... No........................... Subpart YYYY does not
require COMS.
Sec. 63.10(e)(3)........... Excess emissions and Yes.......................... After September 8, 2020
parameter exceedances submitted with the
reports. compliance report
through CEDRI according
to Sec. 63.6150(a).
Sec. 63.10(e)(4)........... Reporting COMS data..... No........................... Subpart YYYY does not
require COMS.
Sec. 63.10(f).............. Waiver for recordkeeping Yes..........................
and reporting.
Sec. 63.11................. Flares.................. No...........................
Sec. 63.12................. State authority and Yes..........................
delegations.
[[Page 13546]]
Sec. 63.13................. Addresses............... Yes.......................... After September 8, 2020
not applicable to
reports required to be
submitted through CEDRI
by 63.6150(c), (e),
(f), or (g).
Sec. 63.14................. Incorporation by Yes..........................
reference.
Sec. 63.15................. Availability of Yes..........................
information.
----------------------------------------------------------------------------------------------------------------
[FR Doc. 2020-02714 Filed 3-6-20; 8:45 am]
BILLING CODE 6560-50-P