Approval and Promulgation of Air Quality Implementation Plans; Pennsylvania; Reasonably Available Control Technology Determinations for Case-by-Case Sources Under the 1997 and 2008 8-Hour Ozone National Ambient Air Quality Standards, 48908-48915 [2021-18752]
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Federal Register / Vol. 86, No. 167 / Wednesday, September 1, 2021 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R03–OAR–2020–0597; FRL–8873–02–
R3]
Approval and Promulgation of Air
Quality Implementation Plans;
Pennsylvania; Reasonably Available
Control Technology Determinations for
Case-by-Case Sources Under the 1997
and 2008 8-Hour Ozone National
Ambient Air Quality Standards
Environmental Protection
Agency (EPA).
ACTION: Final rule.
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AGENCY:
available through https://
www.regulations.gov, or please contact
the person identified in the FOR FURTHER
INFORMATION CONTACT section for
additional availability information.
FOR FURTHER INFORMATION CONTACT: Ms.
Emily Bertram, Permits Branch (3AD10),
Air & Radiation Division, U.S.
Environmental Protection Agency,
Region III, 1650 Arch Street,
Philadelphia, Pennsylvania 19103. The
telephone number is (215) 814–5273.
Ms. Bertram can also be reached via
electronic mail at bertram.emily@
epa.gov.
SUPPLEMENTARY INFORMATION:
I. Background
On February 11, 2021, EPA published
SUMMARY: The Environmental Protection
a notice of proposed rulemaking
Agency (EPA) is approving multiple
(NPRM). 86 FR 9031. In the NPRM, EPA
state implementation plan (SIP)
proposed approval of case-by-case
revisions submitted by the
RACT determinations or alternative
Commonwealth of Pennsylvania. These
NOX emissions limits for eight sources
revisions were submitted by the
included in the subject SIP submission
Pennsylvania Department of
for the 1997 and 2008 8-hour ozone
Environmental Protection (PADEP) to
NAAQS. The case-by-case RACT
establish and require reasonably
available control technology (RACT) for determinations and alternative NOX
emissions limits for these sources were
nine major sources of volatile organic
included in a SIP revision submitted by
compounds (VOC) and/or nitrogen
PADEP on March 9, 2020.
oxides (NOX) pursuant to the
Under certain circumstances, states
Commonwealth of Pennsylvania’s
are
required to submit SIP revisions to
conditionally approved RACT
address RACT requirements for major
regulations. In this rulemaking action,
sources of NOX and VOC, and any
EPA is only approving source-specific
source covered by control technique
(also referred to as ‘‘case-by-case’’)
guidelines (CTG), for each ozone
RACT determinations or alternative
NAAQS. Which NOX and VOC sources
NOX emissions limits for sources at
in Pennsylvania are considered ‘‘major,’’
eight major NOX and VOC emitting
and therefore to be addressed for RACT
facilities within the Commonwealth
revisions, is dependent on the location
submitted by PADEP. These RACT
of each source within the
evaluations were submitted to meet
Commonwealth. Sources located in
RACT requirements for the 1997 and
nonattainment areas would be subject to
2008 8-hour ozone national ambient air
the ‘‘major source’’ definitions
quality standards (NAAQS). EPA is
established under the CAA based on the
approving these revisions to the
area’s current classification(s). In
Pennsylvania SIP in accordance with
Pennsylvania, sources located outside of
the requirements of the Clean Air Act
moderate or above ozone nonattainment
(CAA) and EPA’s implementing
areas are subject to the major source
regulations.
threshold of 50 tons per year (tpy)
DATES: This final rule is effective on
because of the Ozone Transport Region
October 1, 2021.
(OTR) requirements in CAA section
ADDRESSES: EPA has established a
184(b)(2).
On May 16, 2016, PADEP submitted
docket for this action under Docket ID
Number EPA–R03–OAR–2020–0597. All a SIP revision addressing RACT for both
the 1997 and 2008 8-hour ozone
documents in the docket are listed on
NAAQS in Pennsylvania. PADEP’s May
the https://www.regulations.gov
16, 2016 SIP revision intended to
website. Although listed in the index,
address certain outstanding VOC CTG
some information is not publicly
RACT and major source VOC and NOX
available, e.g., confidential business
information (CBI) or other information
RACT requirements for both standards.
whose disclosure is restricted by statute. The SIP revision requested approval of
Certain other material, such as
Pennsylvania’s 25 Pa. Code 129.96–100,
copyrighted material, is not placed on
Additional RACT Requirements for
the internet and will be publicly
Major Sources of NOX and VOCs (the
available only in hard copy form.
‘‘presumptive’’ RACT II rule). Prior to
Publicly available docket materials are
the adoption of the RACT II rule,
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Pennsylvania relied on the NOX and
VOC control measures in 25 Pa. Code
129.92–95, Stationary Sources of NOX
and VOCs, (the RACT I rule) to meet
RACT for major sources of VOC and
NOX. The requirements of the RACT I
rule remain approved into
Pennsylvania’s SIP and continue to be
implemented.1 On September 26, 2017,
PADEP submitted a supplemental SIP
revision, dated September 22, 2017,
which committed to address various
deficiencies identified by EPA in
PADEP’s May 16, 2016 ‘‘presumptive’’
RACT II rule SIP revision.
On May 9, 2019, EPA conditionally
approved the RACT II rule based on the
commitments PADEP made in its
September 22, 2017 supplemental SIP
revision.2 84 FR 20274. In EPA’s final
conditional approval, EPA noted that
PADEP would be required to submit, for
EPA’s approval, SIP revisions to address
any facility-wide or system-wide NOX
emissions averaging plans approved
under 25 Pa. Code 129.98 and any caseby-case RACT determinations under 25
Pa. Code 129.99. PADEP committed to
submitting these additional SIP
revisions within 12 months of EPA’s
final conditional approval, specifically
May 9, 2020. Through multiple
submissions between 2017 and 2020,
PADEP has submitted to EPA for
approval various SIP submissions to
implement its RACT II case-by-case
determinations and alternative NOX
emissions limits. This rulemaking is
based on EPA’s review of one of these
SIP revisions.
II. Summary of SIP Revision and EPA
Analysis
A. Summary of SIP Revision
To satisfy a requirement from EPA’s
May 9, 2019 conditional approval,
PADEP submitted to EPA SIP revisions
addressing alternative NOX emissions
limits and/or case-by-case RACT
requirements for major sources in
Pennsylvania subject to 25 Pa. Code
129.98 or 129.99. In the Pennsylvania
RACT SIP revisions, PADEP included a
case-by-case RACT determination for
the existing emissions units at each of
the major sources of NOX and/or VOC
1 The RACT I Rule was approved by EPA into the
Pennsylvania SIP on March 23, 1998. 63 FR 13789.
Through this rulemaking, certain source-specific
RACT I requirements will be superseded by more
stringent requirements. See Section II of the
preamble to this Final Rule.
2 On August 27, 2020, the Third Circuit Court of
Appeals issued a decision vacating EPA’s approval
of three provisions of Pennsylvania’s presumptive
RACT II rule applicable to certain coal-fired power
plants. Sierra Club v. EPA, 972 F.3d 290 (3d Cir.
2020). None of the sources in this rulemaking are
subject to the three presumptive RACT II provisions
at issue in that Sierra Club decision.
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that required a source-specific RACT
determination or alternative NOX
emissions limits for major sources
seeking such limits.
In PADEP’s case-by-case RACT
determinations, an evaluation was
completed to determine if previously
SIP-approved, case-by-case RACT
emission limits or operational controls
(herein referred to as RACT I and
contained in RACT I permits) were more
stringent than the new RACT II
presumptive or case-by-case
requirements. If more stringent, the
RACT I requirements will continue to
apply to the applicable source. If the
new case-by-case RACT II requirements
are more stringent than the RACT I
requirements, then the RACT II
requirements will supersede the prior
RACT I requirements.3
In PADEP’s RACT determinations
involving NOX averaging, an evaluation
was completed to determine that the
aggregate NOX emissions emitted by the
air contamination sources included in
the facility-wide or system-wide NOX
emissions averaging plan using a 30-day
48909
rolling average are not greater than the
NOX emissions that would be emitted
by the group of included sources if each
source complied with the applicable
presumptive limitation in 25 Pa. Code
129.97 on a source-specific basis.
Here, EPA is taking action on SIP
revisions pertaining to case-by-case
RACT requirements and alternative NOX
emissions limits for eight major sources
of NOX and/or VOC in Pennsylvania, as
summarized in Table 1 in this
document.4
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TABLE 1—EIGHT MAJOR NOX AND/OR VOC SOURCES IN PENNSYLVANIA SUBJECT TO CASE-BY-CASE RACT II
DETERMINATIONS UNDER THE 1997 AND 2008 8-HOUR OZONE NAAQS
Major source
(county)
1-hour ozone RACT
source?
(RACT I)
Major source pollutant
(NOX and/or VOC)
Volvo Construction Equipment North America (Franklin) .............
National Fuel Gas Supply Corporation—Roystone Compressor
Station (Warren).
E.I DuPont de Nemours and Co. (Bradford) ................................
Carmeuse Lime Inc. (Lebanon) ....................................................
Kovatch Mobile Equipment Corp. (Carbon) ..................................
Merck, Sharpe & Dohme Corp. (formerly Merck and Co., Inc.—
West Point Facility) (Montgomery).
Letterkenny Army Depot (formerly Department of the Army)
(Franklin).
Fairless Energy, LLC (Bucks) .......................................................
No ............................
Yes ..........................
VOC ....................................
NOX and VOC ....................
28–05012 (6/1/2019)
62–141H (1/16/2018)
Yes ..........................
Yes ..........................
No ............................
Yes ..........................
NOX and VOC ....................
NOX ....................................
VOC ....................................
NOX and VOC ....................
08–00002 (9/28/2018)
38–05003 (3/6/2019)
13–00008 (10/27/2017)
46–00005 (1/5/2017)
Yes ..........................
VOC ....................................
28–05002 (6/1/2018)
No ............................
NOX and VOC ....................
09–00124 (12/6/2016)
The case-by-case RACT
determinations submitted by PADEP
consist of an evaluation of all
reasonably available controls at the time
of evaluation for each affected emissions
unit, resulting in a PADEP
determination of what specific emission
limit or control measures satisfy RACT
for that particular unit. The adoption of
new, additional, or revised emission
limits or control measures to existing
SIP-approved RACT I requirements
were specified as requirements in new
or revised Federally enforceable permits
(hereafter RACT II permits) issued by
PADEP to the source. Similarly,
PADEP’s determinations of alternative
NOX emissions limits are included in
RACT II permits. These RACT II permits
have been submitted as part of the
Pennsylvania RACT SIP revisions for
EPA’s approval in the Pennsylvania SIP
under 40 CFR 52.2020(d)(1). The RACT
II permits submitted by PADEP are
listed in the last column of Table 1,
along with the permit effective date, and
are part of the docket for this rule,
which is available online at https://
www.regulations.gov, Docket No. EPA–
R03–OAR–2020–0597.5 EPA is
incorporating by reference in the
Pennsylvania SIP, via the RACT II
permits, source-specific RACT emission
limits and control measures and
alternative NOX emissions limits under
the 1997 and 2008 8-hour ozone
NAAQS for certain major sources of
NOX and VOC emissions.
3 While the prior SIP-approved RACT I permit
will remain part of the SIP, this RACT II rule will
incorporate by reference the RACT II requirements
through the RACT II permit and clarify the ongoing
applicability of specific conditions in the RACT I
permit.
4 PADEP’s March 9, 2020 package of SIP revisions
included source-specific RACT II determinations
for sources at nine facilities. As indicated in the
proposed rulemaking, EPA is only acting on eight
of these facilities at this time. EPA will be acting
on sources located at the Montour, LLC facility in
a separate future rulemaking.
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B. EPA’s Final Action
PADEP’s SIP revisions incorporate its
determinations of source-specific RACT
II controls for individual emission units
at major sources of NOX and/or VOC in
Pennsylvania, where those units are not
covered by or cannot meet
Pennsylvania’s presumptive RACT
regulation or where included in a NOX
emissions averaging plan. After
thorough review and evaluation of the
information provided by PADEP in its
SIP revision submittals for sources at
eight major NOX and/or VOC emitting
facilities in Pennsylvania, EPA found
that: (1) PADEP’s case-by-case RACT
determinations and conclusions
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RACT II permit
(effective date)
establish limits and/or controls on
individual sources that are reasonable
and appropriately considered
technically and economically feasible
controls (2) PADEP’s determinations on
alternative NOX emission limits
demonstrate that emissions under the
averaging plan are equivalent to
emissions if the individual sources were
operating in accordance with the
applicable presumptive limit, and (3)
PADEP’s determinations are consistent
with the CAA, EPA regulations, and
applicable EPA guidance.
PADEP, in its RACT II
determinations, considered the prior
source-specific RACT I requirements
and, where more stringent, retained
those RACT I requirements as part of its
new RACT determinations. In the
NPRM, EPA proposed to find that all the
proposed revisions to previously SIPapproved RACT I requirements would
result in equivalent or additional
reductions of NOX and/or VOC
emissions. The proposed revisions
should not interfere with any applicable
requirements concerning attainment of
5 The RACT II permits included in the docket for
this rulemaking are redacted versions of the
facilities’ Federally enforceable permits. They
reflect the specific RACT requirements being
approved into the Pennsylvania SIP via this final
action.
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the NAAQS, reasonable further
progress, or other applicable
requirements under section 110(l) of the
CAA.
Other specific requirements of
Pennsylvania’s 1997 and 2008 8-hour
ozone NAAQS case-by-case RACT
determinations and alternative NOX
emissions limits and the rationale for
EPA’s proposed action were explained
in the NPRM, and its associated
technical support document (TSD), and
will not be restated here.
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III. Public Comments and EPA
Responses
EPA received comments from four
commenters on the February 11, 2021
NPRM. 86 FR 9031. A summary of the
comments and EPA’s response are
discussed in this section. A copy of the
comments can be found in the docket
for this rule action.
Comment 1: The commenter claims
that EPA cannot approve the proposed
Pennsylvania RACT II case-by-case
(CbC) determinations under the 1997
and 2008 8-hour ozone NAAQS because
the CAA section 110(l) analysis is
inadequate. In particular, the
commenter focuses on the proposed
NOX limitations and whether they will
cause or contribute to violations of the
2010 1-hour NOX NAAQS. (The 2010 1hour NAAQS is for oxides of nitrogen,
as measured by nitrogen dioxide (NO2).)
The commenter argues that under CAA
section 110(k)(1)(a) and 40 CFR part 51,
Appendix V, 2.2(d), a state must
demonstrate that the NAAQSs are
protected if a SIP is to be approved and
that Pennsylvania has not made an
adequate demonstration under section
110(l) related to the potential impact of
these RACT determinations on the 2010
1-hour NOX NAAQS. The commenter
then suggests that EPA is unable to
approve Pennsylvania’s CbC RACT II
determinations unless such a
demonstration has been made, even
though the rules reduce NOX emissions.
The commenter highlights their concern
by including results from air dispersion
modeling of NOX emissions from the
Bighorn well pad in Colorado that they
claim shows the potential impact of
NOX emissions on 1-hour NOX NAAQS
violations. The commenter states that
EPA must undertake a modeling
analysis to determine if the proposed
CbC RACT II determinations will cause
or contribute to 2010 1-hour NOX
NAAQS violations. The commenter
indicates that EPA must repropose this
action including any such modeling
information or other information
utilized in the demonstration that the
NAAQS will be protected.
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Response 1: As described in the
proposed rulemaking, Pennsylvania was
required through implementation of the
1997 and 2008 8-hour ozone NAAQS to
determine RACT II requirements for
major NOX and VOC emitting sources
within the Commonwealth. PADEP had
previously established CbC RACT
requirements under the 1979 1-hour
ozone NAAQS.6 PADEP finalized its
overall RACT II program, which
included presumptive RACT for certain
sources, and it was conditionally
approved by EPA.7 As part of the EPA’s
conditional approval, PADEP was
required to complete source-specific
CbC RACT II determinations for subject
NOX or VOC sources that could not
meet the presumptive requirements or
for which a presumptive limit did not
exist. As required by its regulations,
PADEP then conducted a RACT II CbC
analysis examining what air pollution
controls are available for those
individual sources to determine the
lowest emission limit that a particular
source is capable of meeting by the
application of control technology that is
reasonably available considering
technologically and economic
feasibility.8
Through its RACT II CbC
determinations, PADEP has established
NOX and VOC limits and requirements
for various sources that either reaffirm
existing emission limits or makes the
limits more stringent. PADEP submitted
those determinations to EPA as bundled
packages of individual SIP revisions.
EPA is now approving the RACT II CbC
SIP revisions for individual NOX and
VOC sources at eight facilities. For the
reasons explained below, EPA
concludes that the arguments presented
by the commenter do not prohibit
approval of these SIP revisions.
CAA section 110(l) prohibits EPA
from approving a SIP revision if the
revision would ‘‘interfere with any
applicable requirement concerning
attainment and reasonable further
progress . . . or any other applicable
requirement of this chapter.’’ 42 U.S.C.
7410(l). While EPA interprets section
110(l) as applying to all NAAQS that are
in effect, including those for which a
relevant SIP submission may not have
been made, the level of rigor needed for
any CAA section 110(l) demonstration
will vary depending on the nature and
circumstances of the revision. For
6 40
CFR 52.2020(d)(1).
FR 20274 (May 9, 2019).
8 See December 9, 1976 memorandum from Roger
Strelow, Assistant Administrator for Air and Waste
Management, to Regional Administrators,
‘‘Guidance for Determining Acceptability of SIP
Regulations in Non-Attainment Areas,’’ and 44 FR
53762 (September 17, 1979).
7 84
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example, an in-depth section 110(l)
analysis is more appropriate where
there is a reasonable expectation that an
existing SIP standard is being weakened
or that there will be a net emissions
increase because of approval of the SIP
revision under consideration. However,
here, the Pennsylvania CbC RACT II SIP
revisions are either retaining an existing
standard or establishing a more
stringent one. EPA, for these reasons,
did not include a detailed section 110(l)
analysis at the proposal stage. Since the
commenter raised the issue, EPA is
responding in this final action by
explaining why its approval is
consistent with section 110(l).
In circumstances where an existing
SIP standard is being weakened or a net
emissions increase is expected, there are
two generally recognized paths for
satisfying CAA section 110(l). First, a
state may demonstrate through an air
quality modeling analysis that the
revision will not interfere with the
attainment of the NAAQS, reasonable
further progress, or any other applicable
requirement. This is the approach the
commenter claims is required for the
Pennsylvania CbC SIP revisions.
Second, a state may substitute
equivalent or greater emissions
reductions to compensate for any
change to a plan to ensure actual
emissions to the air are not increased
and thus preserve status quo air quality.
A showing that the substitute measures
preserve status quo air quality is
generally sufficient to demonstrate
noninterference through this alternative
approach. Courts have upheld EPA’s
approval of a SIP revision based on a
state’s use of substitute measures.
Kentucky Resources Council, Inc. v.
EPA, 467 F.3d 986 (6th Cir. 2006) and
Indiana v. EPA, 796 F. 3d 803 (7th Cir.
2015).
Both the Kentucky Resources and
Indiana cases involved circumstances
where a state sought to revise provisions
within its SIP related to its vehicle
emissions testing program. In both
situations, the petitioners were
concerned with increased emissions
that might occur due to the changes to
the testing program. The state in each
case justified its SIP revision, in part, by
demonstrating that it had substitute
emission reductions that would fully
compensate for the expected emissions
increase caused by the modifications to
the testing program. The court in each
case upheld EPA’s interpretation of
section 110(l), which allows states to
substitute equivalent emissions
reductions to compensate for any
change to a plan to ensure actual
emissions to the air are not increased
and thus preserve status quo air quality.
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However, again, these two cases are
most relevant in circumstances where
an existing SIP standard is being
weakened or a net emissions increase is
expected, which are not the
circumstances presented by the SIP
revisions that EPA is approving here.
In a more analogous case to the
situation presented here, EPA’s
interpretation of section 110(l) was
upheld in WildEarth Guardians v. EPA,
759 F.3d 1064 (9th Cir. 2014). There, the
court rejected a challenge to an EPA
action approving a regional haze plan
and concluded that WildEarth had
identified ‘‘nothing in [the] SIP that
weakens or removes any pollution
controls. And even if the SIP merely
maintained the status quo, that would
not interfere with the attainment or
maintenance of the NAAQS.’’ 9 For that
reason, the court concluded that
WildEarth had failed to show that EPA’s
approval of the SIP contravened section
110(l). The court’s holding demonstrates
that a SIP approval that does not
weaken or remove pollution controls
would not violate section 110(l).
The WildEarth decision informs the
approach to section 110(l) EPA is taking
to approve the Pennsylvania CbC RACT
SIP revisions. Here, contrary to the
commenter’s characterization,
Pennsylvania is not relaxing standards
or eliminating a program, but rather, is
only re-evaluating the technical and
economic feasibility of air pollution
controls for subject air pollution sources
as required by implementation of the
1997 and 2008 8-hour NAAQS. Based
on that review, the state, as explained in
more detail below, has made
determinations that either retain or
make more stringent existing NOX
emission limits. Emissions are not
expected to increase, and will likely
decrease, as a result of PADEP’s RACT
II NOX CbC determinations and EPA’s
approval hereof. Additionally, the
supporting documents submitted by
PADEP identify numerous NOX sources
that were subject to RACT I but that are
no longer operating and have been
permanently closed. Under these
circumstances, Pennsylvania’s
demonstration to meet the requirements
of section 110(l) for its CbC RACT II
determinations is not one of modeling
or identifying equivalent emissions
reductions to compensate for or offset
an emissions increase because the
revisions are not resulting in emissions
increases, but rather to establish that its
new CbC NOX RACT determinations are
preserving the status quo air quality or
achieving additional reductions beyond
the status quo.
9 Id.
at 1074.
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With this rulemaking action, EPA is
only approving revisions that add
specific NOX and VOC CbC RACT II
determinations to the Pennsylvania SIP.
In the subject RACT II CbC
determinations, PADEP has made an
adequate showing that its CbC
determinations for individual sources at
the eight facilities at issue not only
preserve the status quo air quality, but
likely reduce the cumulative NOX
emissions from the subject sources. As
described in its technical review
memorandums and related documents,
which are included in the docket for
this rulemaking, PADEP evaluated both
the technical and economic feasibility of
various control equipment for these
sources and used that evaluation to
determine the RACT II requirements.
PADEP also considered the prior RACT
I requirements to determine whether the
RACT II requirements were as stringent
as the previously established standards.
In circumstances where the RACT I
requirements were more stringent, they
were retained and remain effective.
Contrary to the commenter’s assertion,
this demonstration included in the
documents in the docket satisfies the
requirements of Part 51, Appendix V.
The record supporting EPA’s approval
of Pennsylvania’s CbC RACT II SIP
revisions is sufficient, so there is no
need to supplement the record. As such,
commenter’s reference to EPA’s
inability to supplement the record, and
to Ober v. U.S. EPA, 84 F.3d 304,312
(9th Cir. 1996), is not applicable to
EPA’s current action.
The facilities addressed in this final
rule breakdown into the categories
listed below.10 As explained in the
proposed rulemaking notice, EPA views
each facility as a separable SIP revision,
and that should it receive comment on
one facility but not others, EPA may
take separate, final action on the
remaining facilities.
Facilities with only VOC sources—
The following facilities are major source
VOC emitting facilities that are minor
sources of NOX. As such, individual
VOC sources at these facilities must
comply with RACT II requirements.
EPA’s approval in this rulemaking for
these facilities only relates to specific
CbC VOC RACT II determinations.
EPA’s approval of the Pennsylvania CbC
VOC RACT II SIP revisions for sources
at these facilities does not involve NOX
emissions, maintains the status quo, and
does not result in an increase in VOC or
10 While the commenter also references a ninth
facility, Montour, LLC, EPA is not acting on
PADEP’s CbC RACT II determination for this
facility at this time. As indicated in the proposed
rulemaking, EPA will be acting on sources located
at this facility in a separate future rulemaking.
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NOX emissions. Therefore, as explained
previously, EPA has determined these
SIP revisions will not interfere with any
applicable requirement concerning
attainment and reasonable further
progress, or any other applicable
requirement of the CAA, pursuant to
section 110(l).
• Kovatch Mobile Equipment Corp
• Letterkenny Army Depot
• Volvo Construction Equipment North
America
Facilities with VOC and NOX Sources
(Only VOC CbC)—The following
facilities are major NOX and VOC
emitting facilities, and individual NOX
and VOC sources at these facilities must
comply with RACT II requirements.
However, EPA’s approval in this
rulemaking for these facilities only
relates to specific CbC VOC RACT II
determinations. EPA’s approval of the
Pennsylvania CbC VOC RACT II SIP
revisions for sources at these facilities
does not involve any NOX emissions,
maintains the status quo, and does not
result in an increase in VOC or NOX
emissions. Therefore, as explained
previously, EPA has determined these
SIP revisions will not interfere with any
applicable requirement concerning
attainment and reasonable further
progress, or any other applicable
requirement of the CAA, pursuant to
section 110(l).
• E.I DuPont de Nemours and Co.
• National Fuel Gas Supply
Corporation—Roystone Compressor
Station
Facilities with CbC NOX Sources—The
following are major NOX emitting
sources and contain individual sources
subject to CbC NOX requirements that
EPA is taking final action on here. More
specific information on those individual
facilities follows:
Carmeuse Lime Inc.—EPA proposed
to approve PADEP’s RACT II CbC NOX
determination for one source at this
facility. The other NOX sources that
were subject to RACT I are now shut
down. In its RACT II determination for
Source 107 (No. 5 Kiln), PADEP
concluded that the use of a low NOX
burner with good combustion and
burner optimization were technically
and economically feasible as RACT and
were incorporated as part of the burner
management plan.11 Based on an
analysis of historical performance
testing data from 2000 to 2017, the
existing short-term emissions limit of
6.0 lbs NOX/ton of lime produced was
reduced to 4.6 lbs NOX/ton of lime
11 See PADEP’s Technical Review Memo, dated
November 19, 2018, which is part of the docket for
this rulemaking.
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produced as a RACT II case-by-case
requirement. A burner management
plan, testing once every five years, and
daily monitoring and recordkeeping of
fuel used hourly were also required.
Through imposition of this more
stringent emission limit along with
related monitoring, testing, and
recordkeeping requirements,
Pennsylvania has demonstrated that the
status quo in NOX emissions has been
maintained, if not improved. As such
EPA’s approval of Pennsylvania’s SIP
revision is adequately justified under
section 110(l).
Merck, Sharpe & Dohme Corp.—EPA
proposed to approve PADEP’s RACT II
CbC NOX determination for two sources
at this facility. Numerous NOX sources
that were subject to RACT I have been
shut down. In its determinations for the
remaining two sources, PADEP has
determined that the RACT II CbC NOX
is continued use of low NOX burners
and good operating practices and
continued compliance with the existing
NOX emission limits.12 Through
retention of the existing emission limits
and continued use of the low NOX
burners, Pennsylvania has demonstrated
that the status quo in NOX emissions
has been maintained. As such, EPA’s
approval of Pennsylvania’s SIP revision
is adequately justified under section
110(l).
Fairless Energy, LLC—EPA proposed
to approve PADEP’s RACT II
determination related to a NOX
averaging plan for four sources at this
facility pursuant to 25 Pa. Code
§ 129.98(a). The averaging plan
provision authorized in section 129.98
allows a facility to establish an
alternative facility-wide or system-wide
RACT NOX emissions limit as long as it
demonstrates that the resulting NOX
emissions using a 30-day rolling average
would not be greater than NOX
emissions from the group of included
sources if they each complied with the
applicable presumptive NOX RACT
emissions limit as individual sources.
Fairless will be averaging the NOX
emissions for four sources to meet the
RACT II requirements, an alternative
emission limit, that will be at least as
stringent as the presumptive emission
limit, which was conditionally
approved by EPA in a prior
rulemaking.13 PADEP’s approval of the
NOX averaging plan ensures that total
12 See PADEP Revised Technical Review Memo,
dated October 9, 2019, which is part of the docket
for this rulemaking action.
13 See 84 FR 20274 (May 9, 2019) as to EPA’s
conditional approval of the presumptive limit and
PADEP’s Technical Review Memo, dated November
29, 2016, as to PADEP’s analysis of the NOX
averaging plan.
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NOX emissions from these sources will
be no greater than the total individual
emissions from each source if each were
to comply with the existing presumptive
emission limit. The NOX averaging plan
also does not eliminate any other
existing non-RACT emission restrictions
applicable to these sources. Through
these measures, Pennsylvania has
demonstrated that the status quo in NOX
emissions has been maintained. As
such, EPA’s approval of PADEP’s SIP
revision is adequately justified under
section 110(l).
As described above, EPA determined
that Pennsylvania had adequately
justified its RACT II CbC NOX
determinations. EPA also concluded,
under section 110(l), that the status quo
in NOX emissions had been maintained,
if not improved and that there is no
need to conduct the modeling suggested
by the commenter. As noted previously,
the commenter included an air
dispersion modeling analysis of NOX
emissions from a well pad at the
Bighorn Pad Facility in Colorado to
highlight an alleged potential of NOX
emissions to cause or contribute to
violations of the 2010 1-hour NOX
NAAQS. The NAAQS for nitrogen
oxides is a 1-hour standard at a level of
100 ppb based on the 3-year average of
98th percentile of the yearly distribution
of 1-hour daily maximum NO2
concentrations. In 2012, EPA designated
areas within Pennsylvania as
attainment/unclassifiable for the 2010
standard.14 The modeling analysis
provided by the commenter indicated
that NOX emissions from the well pad
area in Colorado could have NO2
impacts within 50 kilometers of the
source.
This modeling analysis from Colorado
does not trigger a need for EPA or
Pennsylvania to conduct modeling on
the impact of NOX emissions from each
individual PA CbC RACT source at
issue in this rulemaking in order for
EPA to approve these SIP revisions.
First, as discussed previously, modeling
is not the sole method available to
satisfy section 110(l) requirements.
Second, the differences in the
meteorology, terrain, and facility
configurations between the Bighorn well
pad and the Pennsylvania CbC RACT II
sources are too significant to rely on the
Bighorn facility modeling results to
serve as surrogate modeling indicating
that the Pennsylvania RACT II sources
have the potential to cause exceedances
of the 2010 1-hour NOX NAAQS in
Pennsylvania. The commenter has not
provided any comparison or
information to show why the Bighorn
14 77
PO 00000
FR 9532 (February 17, 2012).
Frm 00026
Fmt 4700
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Pad Facility modeling results should
apply to these specific RACT II sources
in Pennsylvania. Further, the
commenter has not presented any
specific information suggesting the
RACT II CbC NOX determinations for
these specific sources could somehow
lead to violations of the 2010 1-hour
NOX NAAQS. Without a more specific
allegation from the commenter about the
sources in question, the commenter’s
allegations are too speculative in nature
to prevent EPA from approving PADEP’s
RACT II CbC NOX determinations for
sources at the eight subject facilities.
Comment 2: The commenter is
supportive of EPA’s proposed
rulemaking, stating that it will
positively affect citizens in the
Commonwealth of Pennsylvania for
multiple reasons and has suggested
some editorial improvements for future
rulemakings that could aid citizen
comprehension.
Response 2: EPA recognizes the
commenter’s support and suggestions.
EPA will consider such suggestions for
future rulemakings.
Comment 3: The commenter states
that the RACT limit for Carmeuse Lime,
Inc of 4.6 lb/NOX per ton of lime is too
lenient. Additionally, the commenter
asserts the testing requirement to verify
the emissions limit by stack test once
every five years is insufficient and
should have required a Continuous
Emission Monitoring System (CEMS)
unit to monitor instantaneous emissions
from the kiln or established an
emissions profile dependent on a
number of factors that might impact
NOX emissions.
Response 3: As detailed in the facility
files for Carmeuse Lime contained in the
docket for this action, the existing shortterm NOX limit for the No. 5 Kiln
established under RACT I was 6.0 lbs
NOX/ton of lime produced. The RACT II
NOX limit of 4.6 lb/ton approved here
represents a reduction of emissions from
RACT I and was established through a
statistical analysis using 17 years of
historical performance testing data.
PADEP also reviewed the RACT/BACT/
LAER Clearinghouse to determine
emission limits for similar kilns and
found that such limits ranged from 3.59
to 9.98 lb/ton. Based on this information
included in the docket, EPA determined
that the NOX limit of 4.6 lb/ton
comports with the CAA requirements
for RACT.
The requirement for stack testing
every five years is consistent with
Pennsylvania’s RACT II compliance
demonstration requirements in 25 Pa.
Code 129.100, which is a part of
Pennsylvania’s SIP-approved RACT
regulations. Under those regulations, a
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five-year stack testing period for sources
without a CEMS is authorized. In
addition to the stack testing, PADEP’s
RACT II determination includes
requirements for a burner management
plan to ensure good combustion and
burner optimization. It also requires
daily recordkeeping on limestone used,
lime produced, and fuel consumed to
provide a current picture of source
operations.15 The sufficiency of the
stack testing requirement is further
justified in light of a long history of
stack testing on this kiln, which
produced the data that enabled the
lowering of the NOX limit. The RACT II
requirements for Kiln No. 5 are also
consistent with the current National
Emission Standards for Hazardous Air
Pollutants for Lime Manufacturing
Plants, 40 CFR 63, Subpart AAAAA, of
which the source is also subject. Given
the basis of the emissions limit and the
stack testing requirement, plus the
establishment of other burner and daily
recordkeeping requirements, EPA
continues to find PADEP’s analysis
reasonable and is finalizing the RACT
determination for Carmeuse Lime.
Comment 4: The comment requests
that EPA clarify which company is
subject to Permit No. 46–0005, included
as part of EPA’s proposed rulemaking
docket EPA–R03–OAR–2020–0597.
Response 4: Permit No. 46–0005 is the
title V operating permit number for
Merck, Sharp, & Dohme Corp.’s facility
located in West Point, Upper Gwynedd
Township, Montgomery County,
Pennsylvania. The cover page (page 1)
of Permit No. 46–0005 contains
additional owner, plant, owner, and
responsible official contact information
for this facility. Merck, Sharpe, and
Dohme is the company name referred to
in the provisions to be incorporated into
the SIP.
IV. Final Action
EPA is approving case-by-case RACT
determinations and/or alternative NOX
emissions limits for eight sources in
Pennsylvania, as required to meet
obligations pursuant to the 1997 and
2008 8-hour ozone NAAQS, as revisions
to the Pennsylvania SIP.
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V. Incorporation by Reference
In this document, EPA is finalizing
regulatory text that includes
incorporation by reference. In
accordance with requirements of 1 CFR
51.5, EPA is finalizing the incorporation
by reference of source-specific RACT
determinations and alternative NOX
15 See PADEP Technical Review Memo, dated
November 19, 2018, which is part of the docket for
this rulemaking action.
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16:01 Aug 31, 2021
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emissions limits under the 1997 and
2008 8-hour ozone NAAQS for certain
major sources of VOC and NOX in
Pennsylvania. EPA has made, and will
continue to make, these materials
generally available through https://
www.regulations.gov and at the EPA
Region III Office (please contact the
person identified in the FOR FURTHER
INFORMATION CONTACT section of this
preamble for more information).
Therefore, these materials have been
approved by EPA for inclusion in the
SIP, have been incorporated by
reference by EPA into that plan, are
fully federally enforceable under
sections 110 and 113 of the CAA as of
the effective date of the final rule of
EPA’s approval, and will be
incorporated by reference in the next
update to the SIP compilation.16
VI. Statutory and Executive Order
Reviews
A. General Requirements
Under the CAA, the Administrator is
required to approve a SIP submission
that complies with the provisions of the
CAA and applicable Federal regulations.
42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions,
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this action
merely approves state law as meeting
Federal requirements and does not
impose additional requirements beyond
those imposed by state law. For that
reason, this action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
of Management and Budget under
Executive Orders 12866 (58 FR 51735,
October 4, 1993) and 13563 (76 FR 3821,
January 21, 2011);
• Does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• Is certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.);
• Does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
• Does not have federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• Is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
16 62
PO 00000
FR 27968 (May 22, 1997).
Frm 00027
Fmt 4700
Sfmt 4700
48913
• Is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• Is not subject to requirements of
section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
application of those requirements would
be inconsistent with the CAA; and
• Does not provide EPA with the
discretionary authority to address, as
appropriate, disproportionate human
health or environmental effects, using
practicable and legally permissible
methods, under Executive Order 12898
(59 FR 7629, February 16, 1994).
In addition, this rule does not have
tribal implications as specified by
Executive Order 13175 (65 FR 67249,
November 9, 2000), because the SIP is
not approved to apply in Indian country
located in the State, and EPA notes that
it will not impose substantial direct
costs on tribal governments or preempt
tribal law.
B. Submission to Congress and the
Comptroller General
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. Section 804,
however, exempts from section 801 the
following types of rules: Rules of
particular applicability; rules relating to
agency management or personnel; and
rules of agency organization, procedure,
or practice that do not substantially
affect the rights or obligations of nonagency parties. 5 U.S.C. 804(3). Because
this is a rule of particular applicability,
EPA is not required to submit a rule
report regarding this action under
section 801.
C. Petitions for Judicial Review
Under section 307(b)(1) of the CAA,
petitions for judicial review of this
action must be filed in the United States
Court of Appeals for the appropriate
circuit by November 1, 2021. Filing a
petition for reconsideration by the
Administrator of this final rule does not
affect the finality of this action for the
purposes of judicial review nor does it
extend the time within which a petition
for judicial review may be filed, and
shall not postpone the effectiveness of
such rule or action. This action
approving Pennsylvania’s NOX and VOC
RACT requirements for eight facilities
for the 1997 and 2008 8-hour ozone
NAAQS may not be challenged later in
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proceedings to enforce its requirements.
(See section 307(b)(2).)
PART 52—APPROVAL AND
PROMULGATION OF
IMPLEMENTATION PLANS
List of Subjects in 40 CFR Part 52
1. The authority citation for part 52
continues to read as follows:
■
Environmental protection, Air
pollution control, Incorporation by
reference, Nitrogen dioxide, Ozone,
Reporting and recordkeeping
requirements, Volatile organic
compounds.
Authority: 42 U.S.C. 7401 et seq.
Subpart NN—Pennsylvania
2. In § 52.2020, the table in paragraph
(d)(1) is amended by:
■ a. Revising the entries ‘‘Merck and
Co., Inc.—West Point Facility;’’
‘‘National Fuel Gas Supply Corp.—
Roystone Compressor Station;’’ and
‘‘Department of the Army;’’ and
■ b. Adding the following entries at the
end of the table: ‘‘Volvo Construction
■
Dated: August 17, 2021.
Diana Esher,
Acting Regional Administrator, Region III.
For the reasons stated in the
preamble, the EPA amends 40 CFR part
52 as follows:
Name of source
Permit No.
State
effective
date
*
*
Merck and Co., Inc.—West Point Facility .....
*
*
OP–46–0005 Montgomery .....
1/13/97 6/23/00
*
*
National Fuel Gas Supply Corp.—Roystone
Compressor Station.
*
*
OP–62–141F Warren .............
4/1/03
*
*
Department of the Army ................................
*
*
28–02002 Franklin ............
2/3/00
*
*
Volvo Construction Equipment North America.
National Fuel Gas Supply Corporation—
Roystone Compressor Station.
E.I. DuPont de Nemours and Co ..................
*
*
28–05012 Franklin ............
6/1/19
Warren .............
1/16/18
08–00002
Bradford ...........
9/28/18
Carmeuse Lime Inc .......................................
38–05003
Lebanon ...........
3/6/19
Kovatch Mobile Equipment Corp ..................
13–00008
Carbon .............
10/27/17
Merck, Sharpe & Dohme Corp. (formerly referenced as Merck and Co., Inc.—West
Point Facility).
Letterkenny Army Depot (formerly referenced as Department of the Army).
Fairless Energy, LLC ....................................
46–00005
Montgomery .....
1/5/17
28–05002
Franklin ............
6/1/18
09–00124
Bucks ...............
12/6/16
*
*
*
*
3. Amend § 52.2064 by adding
paragraph (d) to read as follows:
■
§ 52.2064 EPA-Approved Source Specific
Reasonably Available Control Technology
(RACT) for Volatile Organic Compounds
(VOC) and Oxides of Nitrogen (NOX).
*
*
*
*
*
(d) Approval of source-specific RACT
requirements for 1997 and 2008 8-hour
ozone national ambient air quality
standards for the facilities listed below
are incorporated as specified below.
(Rulemaking Docket No. EPA–OAR–
2020–0597).
(1) Volvo Construction Equipment
North America, LLC.—Incorporating by
reference Permit No. 28–05012, effective
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Frm 00028
Fmt 4700
*
Sfmt 4700
Identification of plan.
*
*
(d) * * *
(1) * * *
*
EPA
approval
date
*
Additional
explanations/§§ 52.2063
and
52.2064 citations 1
*
*
4/18/01, 66 FR 19858 ................
*
See also 52.2064(d)(6).
*
*
10/27/04, 69 FR 62583 ..............
*
See also 52.2064(d)(2).
*
*
3/31/05, 70 FR 16416 ................
*
See also 52.2064(d)(7).
*
Federal Register
*
52.2064(d)(1).
Federal Register
52.2064(d)(2).
Federal Register
52.2064(d)(3).
Federal Register
52.2064(d)(4).
Federal Register
52.2064(d)(5).
Federal Register
52.2064(d)(6).
9/1/21, [insert Federal Register
citation].
9/1/21, [insert Federal Register
citation].
52.2064(d)(7).
9/1/21, [insert
citation].
9/1/21, [insert
citation].
9/1/21, [insert
citation].
9/1/21, [insert
citation].
9/1/21, [insert
citation].
9/1/21, [insert
citation].
June 1, 2019, as redacted by
Pennsylvania.
(2) National Fuel Gas Supply
Corporation Roystone Compressor
Station—Incorporating by reference
Permit No. 62–141H, effective January
16, 2018, as redacted by Pennsylvania.
All permit conditions in the prior RACT
Permit No. OP–62–141F, effective April
1, 2003, remain as RACT requirements
except for the Penneco boiler (1.5
MMBtu/hr) and Struthers boiler (2.5
MMBtu/hr), which are no longer in
operation. See also
§ 52.2063(c)(213)(i)(B)(1) for prior RACT
approval.
(3) E.I. DuPont de Nemours and
Company—Incorporating by reference
Permit No. 08–00002, effective
PO 00000
§ 52.2020
*
62–141H
*
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County
Equipment North America;’’ ‘‘National
Fuel Gas Supply Corporation—Roystone
Compressor Station;’’ ‘‘E.I. DuPont de
Nemours and Co.;’’ ‘‘Carmeuse Lime
Inc.;’’ ‘‘Kovatch Mobile Equipment
Corp.;’’ ‘‘Merck, Sharpe & Dohme Corp.
(formerly referenced as Merck and Co.,
Inc.—West Point Facility);’’
‘‘Letterkenny Army Depot (formerly
referenced as Department of the Army);’’
‘‘Fairless Energy, LLC.’’
The revisions and additions read as
follows:
52.2064(d)(8).
September 28, 2018, as redacted by
Pennsylvania.
(4) Carmeuse Lime, Inc—
Incorporating by reference Permit No.
38–05003, effective March 6, 2019, as
redacted by Pennsylvania.
(5) Kovatch Mobile Equipment
Corporation—Incorporating by reference
Permit No. 13–00008, effective October
27, 2017, as redacted by Pennsylvania.
(6) Merck, Sharp & Dohme
Corporation—Incorporating by reference
Permit No. 46–00005, issued January 5,
2017, as redacted by Pennsylvania,
which supersedes the prior RACT
Permit No. OP–46–0005, issued January
13, 1997 and revised June 23, 2000,
except for the following conditions,
which remain as a RACT requirements
applicable to the following sources:
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Conditions #4A, #9C, and #13D for
boiler 3 (Source ID 033); conditions
#4A, #9C, and #13D for boiler 5 (Source
ID 035); conditions #4B and #9 for the
gas turbine (Source ID 039); conditions
#6A, #6B, and #6D for any remaining
shell freezers (Source ID 105);
conditions #6A and #6D for air
emissions (disinfection; Source IDs 105,
107, 108, and 111); conditions #4C and
#9 for any remaining generators (various
Source IDs); condition #8 for research
and development (Section C); and
condition #11 for any remaining
deminimus sources (Section C). See also
§ 52.2063(c)(154)(i)(D) for prior RACT
approval.
(7) Letterkenny Army Depot—
Incorporating by reference Permit No.
28–05002, effective June 1, 2018, as
redacted by Pennsylvania, which
supersedes the prior RACT Permit No.
28–02002, effective February 3, 2000
except for conditions 5, 6, 7, 8, 9, 10,
11, 12, and 14 which also remain as
RACT requirements. See also
§ 52.2063(d)(1)(g) for prior RACT
approval.
(8) Fairless Energy, LLC—
Incorporating by reference Permit No.
09–00124, effective December 6, 2016 as
redacted by Pennsylvania.
[FR Doc. 2021–18752 Filed 8–31–21; 8:45 am]
BILLING CODE 6560–50–P
GENERAL SERVICES
ADMINISTRATION
48 CFR Part 570
[GSAR Case 2021–G524; Docket No. GSA–
GSAR 2021–0019; Sequence No. 1]
RIN 3090–AK49
General Services Administration
Acquisition Regulation (GSAR);
Updates to Certain Online References
in the GSAM
Office of Acquisition Policy,
General Services Administration (GSA).
ACTION: Final rule.
AGENCY:
The General Services
Administration (GSA) is issuing a final
rule amending the General Services
Administration Acquisition Regulation
(GSAR) to update an outdated reference
to a legacy website.
DATES: Effective October 1, 2021.
FOR FURTHER INFORMATION CONTACT: Mr.
Tyler Piper or Mr. Stephen Carroll at
817–253–7858 or gsarpolicy@gsa.gov,
for clarification of content. For
information pertaining to status or
publication schedules, contact the
Regulatory Secretariat at 202–501–4755.
Please cite GSAR Case 2021–G524.
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SUMMARY:
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16:01 Aug 31, 2021
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48915
SUPPLEMENTARY INFORMATION:
VI. Notice for Public Comment
I. Background
The statute that applies to the
publication of the GSAR is the Office of
Federal Procurement Policy statute
(codified at title 41 of the United States
Code). Specifically, 41 U.S.C. 1707(a)(1)
requires that a procurement policy,
regulation, procedure or form (including
an amendment or modification thereof)
must be published for public comment
if it relates to the expenditure of
appropriated funds, and has either a
significant effect beyond the internal
operating procedures of the agency
issuing the policy, regulation,
procedure, or form, or has a significant
cost or administrative impact on
contractors or offerors. This rule is not
required to be published for public
comment, because it does not have a
significant effect or impose any new
requirements on contractors or offerors.
The rule simply replaces website
references.
GSA’s Integrated Award Environment
integrated the legacy SAM.gov into the
beta.SAM.gov environment on May 24,
2021, migrating the functionality of
SAM.gov into beta.SAM.gov. The term
‘‘beta’’ is retired, and there is now only
one SAM.gov.
II. Authority for This Rulemaking
Title 40 of the United States Code
(U.S.C.) Section 121 authorizes GSA to
issue regulations, including the GSAR,
to control the relationship between GSA
and contractors.
III. Discussion and Analysis
The System for Award Management
(SAM) has officially gone live, and as
such the URL to reach it has changed
from https://beta.sam.gov to https://
www.sam.gov. This rule simply updates
an outdated URL reference to the new
website.
IV. Executive Orders 12866 and 13563
Executive Orders (E.O.s) 12866 and
13563 direct agencies to assess all costs
and benefits of available regulatory
alternatives and, if regulation is
necessary, to select regulatory
approaches that maximize net benefits
(including potential economic,
environmental, public health and safety
effects, distributive impacts, and
equity). E.O. 13563 emphasizes the
importance of quantifying both costs
and benefits, of reducing costs, of
harmonizing rules, and of promoting
flexibility. This rule has been reviewed
and determined by OMB not to be a
significant regulatory action and,
therefore, was not subject to review
under section 6(b) of E.O. 12866,
Regulatory Planning and Review, dated
September 30, 1993.
V. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., as amended by the
Small Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a ‘‘major rule’’ may take
effect, the agency promulgating the rule
must submit a rule report, which
includes a copy of the rule, to each
House of the Congress and to the
Comptroller General of the United
States. A major rule cannot take effect
until 60 days after it is published in the
Federal Register. This rule has been
reviewed and determined by OMB not
to be a ‘‘major rule’’ under 5 U.S.C.
804(2).
PO 00000
Frm 00029
Fmt 4700
Sfmt 4700
VII. Regulatory Flexibility Act
The Regulatory Flexibility Act (5
U.S.C. 601 et seq.) does not apply to this
rule, because an opportunity for public
comment is not required to be given for
this rule under 41 U.S.C. 1707(a)(1) (see
Section VI. of this preamble).
Accordingly, no regulatory flexibility
analysis is required and none has been
prepared.
VIII. Paperwork Reduction Act
This rule does not contain any
information collection requirements that
require the approval of the Office of
Management and Budget under the
Paperwork Reduction Act (44 U.S.C.
chapter 35).
List of Subjects in 48 CFR Part 570
Government procurement.
Jeffrey Koses,
Senior Procurement Executive, Office of
Acquisition Policy, Office of Governmentwide Policy, General Services Administration.
Therefore, GSA amends 48 CFR part
570 as set forth below:
PART 570—ACQUIRING LEASEHOLD
INTERESTS IN REAL PROPERTY
1. The authority citation for part 570
continues to read as follows:
■
Authority: 40 U.S.C. 121(c).
570.106
[Amended]
2. Amend section 570.106 in
paragraph (a) by removing
‘‘Governmentwide Point of Entry (GPE)
at https://beta.sam.gov or successor
system’’ and adding ‘‘System for Award
■
E:\FR\FM\01SER1.SGM
01SER1
Agencies
[Federal Register Volume 86, Number 167 (Wednesday, September 1, 2021)]
[Rules and Regulations]
[Pages 48908-48915]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2021-18752]
[[Page 48908]]
=======================================================================
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R03-OAR-2020-0597; FRL-8873-02-R3]
Approval and Promulgation of Air Quality Implementation Plans;
Pennsylvania; Reasonably Available Control Technology Determinations
for Case-by-Case Sources Under the 1997 and 2008 8-Hour Ozone National
Ambient Air Quality Standards
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
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SUMMARY: The Environmental Protection Agency (EPA) is approving
multiple state implementation plan (SIP) revisions submitted by the
Commonwealth of Pennsylvania. These revisions were submitted by the
Pennsylvania Department of Environmental Protection (PADEP) to
establish and require reasonably available control technology (RACT)
for nine major sources of volatile organic compounds (VOC) and/or
nitrogen oxides (NOX) pursuant to the Commonwealth of
Pennsylvania's conditionally approved RACT regulations. In this
rulemaking action, EPA is only approving source-specific (also referred
to as ``case-by-case'') RACT determinations or alternative
NOX emissions limits for sources at eight major
NOX and VOC emitting facilities within the Commonwealth
submitted by PADEP. These RACT evaluations were submitted to meet RACT
requirements for the 1997 and 2008 8-hour ozone national ambient air
quality standards (NAAQS). EPA is approving these revisions to the
Pennsylvania SIP in accordance with the requirements of the Clean Air
Act (CAA) and EPA's implementing regulations.
DATES: This final rule is effective on October 1, 2021.
ADDRESSES: EPA has established a docket for this action under Docket ID
Number EPA-R03-OAR-2020-0597. All documents in the docket are listed on
the https://www.regulations.gov website. Although listed in the index,
some information is not publicly available, e.g., confidential business
information (CBI) 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 through
https://www.regulations.gov, or please contact the person identified in
the FOR FURTHER INFORMATION CONTACT section for additional availability
information.
FOR FURTHER INFORMATION CONTACT: Ms. Emily Bertram, Permits Branch
(3AD10), Air & Radiation Division, U.S. Environmental Protection
Agency, Region III, 1650 Arch Street, Philadelphia, Pennsylvania 19103.
The telephone number is (215) 814-5273. Ms. Bertram can also be reached
via electronic mail at [email protected].
SUPPLEMENTARY INFORMATION:
I. Background
On February 11, 2021, EPA published a notice of proposed rulemaking
(NPRM). 86 FR 9031. In the NPRM, EPA proposed approval of case-by-case
RACT determinations or alternative NOX emissions limits for
eight sources included in the subject SIP submission for the 1997 and
2008 8-hour ozone NAAQS. The case-by-case RACT determinations and
alternative NOX emissions limits for these sources were
included in a SIP revision submitted by PADEP on March 9, 2020.
Under certain circumstances, states are required to submit SIP
revisions to address RACT requirements for major sources of
NOX and VOC, and any source covered by control technique
guidelines (CTG), for each ozone NAAQS. Which NOX and VOC
sources in Pennsylvania are considered ``major,'' and therefore to be
addressed for RACT revisions, is dependent on the location of each
source within the Commonwealth. Sources located in nonattainment areas
would be subject to the ``major source'' definitions established under
the CAA based on the area's current classification(s). In Pennsylvania,
sources located outside of moderate or above ozone nonattainment areas
are subject to the major source threshold of 50 tons per year (tpy)
because of the Ozone Transport Region (OTR) requirements in CAA section
184(b)(2).
On May 16, 2016, PADEP submitted a SIP revision addressing RACT for
both the 1997 and 2008 8-hour ozone NAAQS in Pennsylvania. PADEP's May
16, 2016 SIP revision intended to address certain outstanding VOC CTG
RACT and major source VOC and NOX RACT requirements for both
standards. The SIP revision requested approval of Pennsylvania's 25 Pa.
Code 129.96-100, Additional RACT Requirements for Major Sources of
NOX and VOCs (the ``presumptive'' RACT II rule). Prior to
the adoption of the RACT II rule, Pennsylvania relied on the
NOX and VOC control measures in 25 Pa. Code 129.92-95,
Stationary Sources of NOX and VOCs, (the RACT I rule) to
meet RACT for major sources of VOC and NOX. The requirements
of the RACT I rule remain approved into Pennsylvania's SIP and continue
to be implemented.\1\ On September 26, 2017, PADEP submitted a
supplemental SIP revision, dated September 22, 2017, which committed to
address various deficiencies identified by EPA in PADEP's May 16, 2016
``presumptive'' RACT II rule SIP revision.
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\1\ The RACT I Rule was approved by EPA into the Pennsylvania
SIP on March 23, 1998. 63 FR 13789. Through this rulemaking, certain
source-specific RACT I requirements will be superseded by more
stringent requirements. See Section II of the preamble to this Final
Rule.
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On May 9, 2019, EPA conditionally approved the RACT II rule based
on the commitments PADEP made in its September 22, 2017 supplemental
SIP revision.\2\ 84 FR 20274. In EPA's final conditional approval, EPA
noted that PADEP would be required to submit, for EPA's approval, SIP
revisions to address any facility-wide or system-wide NOX
emissions averaging plans approved under 25 Pa. Code 129.98 and any
case-by-case RACT determinations under 25 Pa. Code 129.99. PADEP
committed to submitting these additional SIP revisions within 12 months
of EPA's final conditional approval, specifically May 9, 2020. Through
multiple submissions between 2017 and 2020, PADEP has submitted to EPA
for approval various SIP submissions to implement its RACT II case-by-
case determinations and alternative NOX emissions limits.
This rulemaking is based on EPA's review of one of these SIP revisions.
---------------------------------------------------------------------------
\2\ On August 27, 2020, the Third Circuit Court of Appeals
issued a decision vacating EPA's approval of three provisions of
Pennsylvania's presumptive RACT II rule applicable to certain coal-
fired power plants. Sierra Club v. EPA, 972 F.3d 290 (3d Cir. 2020).
None of the sources in this rulemaking are subject to the three
presumptive RACT II provisions at issue in that Sierra Club
decision.
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II. Summary of SIP Revision and EPA Analysis
A. Summary of SIP Revision
To satisfy a requirement from EPA's May 9, 2019 conditional
approval, PADEP submitted to EPA SIP revisions addressing alternative
NOX emissions limits and/or case-by-case RACT requirements
for major sources in Pennsylvania subject to 25 Pa. Code 129.98 or
129.99. In the Pennsylvania RACT SIP revisions, PADEP included a case-
by-case RACT determination for the existing emissions units at each of
the major sources of NOX and/or VOC
[[Page 48909]]
that required a source-specific RACT determination or alternative
NOX emissions limits for major sources seeking such limits.
In PADEP's case-by-case RACT determinations, an evaluation was
completed to determine if previously SIP-approved, case-by-case RACT
emission limits or operational controls (herein referred to as RACT I
and contained in RACT I permits) were more stringent than the new RACT
II presumptive or case-by-case requirements. If more stringent, the
RACT I requirements will continue to apply to the applicable source. If
the new case-by-case RACT II requirements are more stringent than the
RACT I requirements, then the RACT II requirements will supersede the
prior RACT I requirements.\3\
---------------------------------------------------------------------------
\3\ While the prior SIP-approved RACT I permit will remain part
of the SIP, this RACT II rule will incorporate by reference the RACT
II requirements through the RACT II permit and clarify the ongoing
applicability of specific conditions in the RACT I permit.
---------------------------------------------------------------------------
In PADEP's RACT determinations involving NOX averaging,
an evaluation was completed to determine that the aggregate
NOX emissions emitted by the air contamination sources
included in the facility-wide or system-wide NOX emissions
averaging plan using a 30-day rolling average are not greater than the
NOX emissions that would be emitted by the group of included
sources if each source complied with the applicable presumptive
limitation in 25 Pa. Code 129.97 on a source-specific basis.
Here, EPA is taking action on SIP revisions pertaining to case-by-
case RACT requirements and alternative NOX emissions limits
for eight major sources of NOX and/or VOC in Pennsylvania,
as summarized in Table 1 in this document.\4\
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\4\ PADEP's March 9, 2020 package of SIP revisions included
source-specific RACT II determinations for sources at nine
facilities. As indicated in the proposed rulemaking, EPA is only
acting on eight of these facilities at this time. EPA will be acting
on sources located at the Montour, LLC facility in a separate future
rulemaking.
Table 1--Eight Major NOX and/or VOC Sources In Pennsylvania Subject to Case-by-Case RACT II Determinations Under the 1997 and 2008 8-Hour Ozone NAAQS
--------------------------------------------------------------------------------------------------------------------------------------------------------
RACT II permit
Major source (county) 1-hour ozone RACT source? (RACT I) Major source pollutant (NOX and/or VOC) (effective date)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Volvo Construction Equipment North No................................... VOC.......................................... 28-05012 (6/1/2019)
America (Franklin).
National Fuel Gas Supply Corporation-- Yes.................................. NOX and VOC.................................. 62-141H (1/16/2018)
Roystone Compressor Station (Warren).
E.I DuPont de Nemours and Co. (Bradford). Yes.................................. NOX and VOC.................................. 08-00002 (9/28/2018)
Carmeuse Lime Inc. (Lebanon)............. Yes.................................. NOX.......................................... 38-05003 (3/6/2019)
Kovatch Mobile Equipment Corp. (Carbon).. No................................... VOC.......................................... 13-00008 (10/27/2017)
Merck, Sharpe & Dohme Corp. (formerly Yes.................................. NOX and VOC.................................. 46-00005 (1/5/2017)
Merck and Co., Inc.--West Point
Facility) (Montgomery).
Letterkenny Army Depot (formerly Yes.................................. VOC.......................................... 28-05002 (6/1/2018)
Department of the Army) (Franklin).
Fairless Energy, LLC (Bucks)............. No................................... NOX and VOC.................................. 09-00124 (12/6/2016)
--------------------------------------------------------------------------------------------------------------------------------------------------------
The case-by-case RACT determinations submitted by PADEP consist of
an evaluation of all reasonably available controls at the time of
evaluation for each affected emissions unit, resulting in a PADEP
determination of what specific emission limit or control measures
satisfy RACT for that particular unit. The adoption of new, additional,
or revised emission limits or control measures to existing SIP-approved
RACT I requirements were specified as requirements in new or revised
Federally enforceable permits (hereafter RACT II permits) issued by
PADEP to the source. Similarly, PADEP's determinations of alternative
NOX emissions limits are included in RACT II permits. These
RACT II permits have been submitted as part of the Pennsylvania RACT
SIP revisions for EPA's approval in the Pennsylvania SIP under 40 CFR
52.2020(d)(1). The RACT II permits submitted by PADEP are listed in the
last column of Table 1, along with the permit effective date, and are
part of the docket for this rule, which is available online at https://www.regulations.gov, Docket No. EPA-R03-OAR-2020-0597.\5\ EPA is
incorporating by reference in the Pennsylvania SIP, via the RACT II
permits, source-specific RACT emission limits and control measures and
alternative NOX emissions limits under the 1997 and 2008 8-
hour ozone NAAQS for certain major sources of NOX and VOC
emissions.
---------------------------------------------------------------------------
\5\ The RACT II permits included in the docket for this
rulemaking are redacted versions of the facilities' Federally
enforceable permits. They reflect the specific RACT requirements
being approved into the Pennsylvania SIP via this final action.
---------------------------------------------------------------------------
B. EPA's Final Action
PADEP's SIP revisions incorporate its determinations of source-
specific RACT II controls for individual emission units at major
sources of NOX and/or VOC in Pennsylvania, where those units
are not covered by or cannot meet Pennsylvania's presumptive RACT
regulation or where included in a NOX emissions averaging
plan. After thorough review and evaluation of the information provided
by PADEP in its SIP revision submittals for sources at eight major
NOX and/or VOC emitting facilities in Pennsylvania, EPA
found that: (1) PADEP's case-by-case RACT determinations and
conclusions establish limits and/or controls on individual sources that
are reasonable and appropriately considered technically and
economically feasible controls (2) PADEP's determinations on
alternative NOX emission limits demonstrate that emissions
under the averaging plan are equivalent to emissions if the individual
sources were operating in accordance with the applicable presumptive
limit, and (3) PADEP's determinations are consistent with the CAA, EPA
regulations, and applicable EPA guidance.
PADEP, in its RACT II determinations, considered the prior source-
specific RACT I requirements and, where more stringent, retained those
RACT I requirements as part of its new RACT determinations. In the
NPRM, EPA proposed to find that all the proposed revisions to
previously SIP-approved RACT I requirements would result in equivalent
or additional reductions of NOX and/or VOC emissions. The
proposed revisions should not interfere with any applicable
requirements concerning attainment of
[[Page 48910]]
the NAAQS, reasonable further progress, or other applicable
requirements under section 110(l) of the CAA.
Other specific requirements of Pennsylvania's 1997 and 2008 8-hour
ozone NAAQS case-by-case RACT determinations and alternative
NOX emissions limits and the rationale for EPA's proposed
action were explained in the NPRM, and its associated technical support
document (TSD), and will not be restated here.
III. Public Comments and EPA Responses
EPA received comments from four commenters on the February 11, 2021
NPRM. 86 FR 9031. A summary of the comments and EPA's response are
discussed in this section. A copy of the comments can be found in the
docket for this rule action.
Comment 1: The commenter claims that EPA cannot approve the
proposed Pennsylvania RACT II case-by-case (CbC) determinations under
the 1997 and 2008 8-hour ozone NAAQS because the CAA section 110(l)
analysis is inadequate. In particular, the commenter focuses on the
proposed NOX limitations and whether they will cause or
contribute to violations of the 2010 1-hour NOX NAAQS. (The
2010 1-hour NAAQS is for oxides of nitrogen, as measured by nitrogen
dioxide (NO2).) The commenter argues that under CAA section
110(k)(1)(a) and 40 CFR part 51, Appendix V, 2.2(d), a state must
demonstrate that the NAAQSs are protected if a SIP is to be approved
and that Pennsylvania has not made an adequate demonstration under
section 110(l) related to the potential impact of these RACT
determinations on the 2010 1-hour NOX NAAQS. The commenter
then suggests that EPA is unable to approve Pennsylvania's CbC RACT II
determinations unless such a demonstration has been made, even though
the rules reduce NOX emissions. The commenter highlights
their concern by including results from air dispersion modeling of
NOX emissions from the Bighorn well pad in Colorado that
they claim shows the potential impact of NOX emissions on 1-
hour NOX NAAQS violations. The commenter states that EPA
must undertake a modeling analysis to determine if the proposed CbC
RACT II determinations will cause or contribute to 2010 1-hour
NOX NAAQS violations. The commenter indicates that EPA must
repropose this action including any such modeling information or other
information utilized in the demonstration that the NAAQS will be
protected.
Response 1: As described in the proposed rulemaking, Pennsylvania
was required through implementation of the 1997 and 2008 8-hour ozone
NAAQS to determine RACT II requirements for major NOX and
VOC emitting sources within the Commonwealth. PADEP had previously
established CbC RACT requirements under the 1979 1-hour ozone NAAQS.\6\
PADEP finalized its overall RACT II program, which included presumptive
RACT for certain sources, and it was conditionally approved by EPA.\7\
As part of the EPA's conditional approval, PADEP was required to
complete source-specific CbC RACT II determinations for subject
NOX or VOC sources that could not meet the presumptive
requirements or for which a presumptive limit did not exist. As
required by its regulations, PADEP then conducted a RACT II CbC
analysis examining what air pollution controls are available for those
individual sources to determine the lowest emission limit that a
particular source is capable of meeting by the application of control
technology that is reasonably available considering technologically and
economic feasibility.\8\
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\6\ 40 CFR 52.2020(d)(1).
\7\ 84 FR 20274 (May 9, 2019).
\8\ See December 9, 1976 memorandum from Roger Strelow,
Assistant Administrator for Air and Waste Management, to Regional
Administrators, ``Guidance for Determining Acceptability of SIP
Regulations in Non-Attainment Areas,'' and 44 FR 53762 (September
17, 1979).
---------------------------------------------------------------------------
Through its RACT II CbC determinations, PADEP has established
NOX and VOC limits and requirements for various sources that
either reaffirm existing emission limits or makes the limits more
stringent. PADEP submitted those determinations to EPA as bundled
packages of individual SIP revisions. EPA is now approving the RACT II
CbC SIP revisions for individual NOX and VOC sources at
eight facilities. For the reasons explained below, EPA concludes that
the arguments presented by the commenter do not prohibit approval of
these SIP revisions.
CAA section 110(l) prohibits EPA from approving a SIP revision if
the revision would ``interfere with any applicable requirement
concerning attainment and reasonable further progress . . . or any
other applicable requirement of this chapter.'' 42 U.S.C. 7410(l).
While EPA interprets section 110(l) as applying to all NAAQS that are
in effect, including those for which a relevant SIP submission may not
have been made, the level of rigor needed for any CAA section 110(l)
demonstration will vary depending on the nature and circumstances of
the revision. For example, an in-depth section 110(l) analysis is more
appropriate where there is a reasonable expectation that an existing
SIP standard is being weakened or that there will be a net emissions
increase because of approval of the SIP revision under consideration.
However, here, the Pennsylvania CbC RACT II SIP revisions are either
retaining an existing standard or establishing a more stringent one.
EPA, for these reasons, did not include a detailed section 110(l)
analysis at the proposal stage. Since the commenter raised the issue,
EPA is responding in this final action by explaining why its approval
is consistent with section 110(l).
In circumstances where an existing SIP standard is being weakened
or a net emissions increase is expected, there are two generally
recognized paths for satisfying CAA section 110(l). First, a state may
demonstrate through an air quality modeling analysis that the revision
will not interfere with the attainment of the NAAQS, reasonable further
progress, or any other applicable requirement. This is the approach the
commenter claims is required for the Pennsylvania CbC SIP revisions.
Second, a state may substitute equivalent or greater emissions
reductions to compensate for any change to a plan to ensure actual
emissions to the air are not increased and thus preserve status quo air
quality. A showing that the substitute measures preserve status quo air
quality is generally sufficient to demonstrate noninterference through
this alternative approach. Courts have upheld EPA's approval of a SIP
revision based on a state's use of substitute measures. Kentucky
Resources Council, Inc. v. EPA, 467 F.3d 986 (6th Cir. 2006) and
Indiana v. EPA, 796 F. 3d 803 (7th Cir. 2015).
Both the Kentucky Resources and Indiana cases involved
circumstances where a state sought to revise provisions within its SIP
related to its vehicle emissions testing program. In both situations,
the petitioners were concerned with increased emissions that might
occur due to the changes to the testing program. The state in each case
justified its SIP revision, in part, by demonstrating that it had
substitute emission reductions that would fully compensate for the
expected emissions increase caused by the modifications to the testing
program. The court in each case upheld EPA's interpretation of section
110(l), which allows states to substitute equivalent emissions
reductions to compensate for any change to a plan to ensure actual
emissions to the air are not increased and thus preserve status quo air
quality.
[[Page 48911]]
However, again, these two cases are most relevant in circumstances
where an existing SIP standard is being weakened or a net emissions
increase is expected, which are not the circumstances presented by the
SIP revisions that EPA is approving here.
In a more analogous case to the situation presented here, EPA's
interpretation of section 110(l) was upheld in WildEarth Guardians v.
EPA, 759 F.3d 1064 (9th Cir. 2014). There, the court rejected a
challenge to an EPA action approving a regional haze plan and concluded
that WildEarth had identified ``nothing in [the] SIP that weakens or
removes any pollution controls. And even if the SIP merely maintained
the status quo, that would not interfere with the attainment or
maintenance of the NAAQS.'' \9\ For that reason, the court concluded
that WildEarth had failed to show that EPA's approval of the SIP
contravened section 110(l). The court's holding demonstrates that a SIP
approval that does not weaken or remove pollution controls would not
violate section 110(l).
---------------------------------------------------------------------------
\9\ Id. at 1074.
---------------------------------------------------------------------------
The WildEarth decision informs the approach to section 110(l) EPA
is taking to approve the Pennsylvania CbC RACT SIP revisions. Here,
contrary to the commenter's characterization, Pennsylvania is not
relaxing standards or eliminating a program, but rather, is only re-
evaluating the technical and economic feasibility of air pollution
controls for subject air pollution sources as required by
implementation of the 1997 and 2008 8-hour NAAQS. Based on that review,
the state, as explained in more detail below, has made determinations
that either retain or make more stringent existing NOX
emission limits. Emissions are not expected to increase, and will
likely decrease, as a result of PADEP's RACT II NOX CbC
determinations and EPA's approval hereof. Additionally, the supporting
documents submitted by PADEP identify numerous NOX sources
that were subject to RACT I but that are no longer operating and have
been permanently closed. Under these circumstances, Pennsylvania's
demonstration to meet the requirements of section 110(l) for its CbC
RACT II determinations is not one of modeling or identifying equivalent
emissions reductions to compensate for or offset an emissions increase
because the revisions are not resulting in emissions increases, but
rather to establish that its new CbC NOX RACT determinations
are preserving the status quo air quality or achieving additional
reductions beyond the status quo.
With this rulemaking action, EPA is only approving revisions that
add specific NOX and VOC CbC RACT II determinations to the
Pennsylvania SIP. In the subject RACT II CbC determinations, PADEP has
made an adequate showing that its CbC determinations for individual
sources at the eight facilities at issue not only preserve the status
quo air quality, but likely reduce the cumulative NOX
emissions from the subject sources. As described in its technical
review memorandums and related documents, which are included in the
docket for this rulemaking, PADEP evaluated both the technical and
economic feasibility of various control equipment for these sources and
used that evaluation to determine the RACT II requirements. PADEP also
considered the prior RACT I requirements to determine whether the RACT
II requirements were as stringent as the previously established
standards. In circumstances where the RACT I requirements were more
stringent, they were retained and remain effective. Contrary to the
commenter's assertion, this demonstration included in the documents in
the docket satisfies the requirements of Part 51, Appendix V. The
record supporting EPA's approval of Pennsylvania's CbC RACT II SIP
revisions is sufficient, so there is no need to supplement the record.
As such, commenter's reference to EPA's inability to supplement the
record, and to Ober v. U.S. EPA, 84 F.3d 304,312 (9th Cir. 1996), is
not applicable to EPA's current action.
The facilities addressed in this final rule breakdown into the
categories listed below.\10\ As explained in the proposed rulemaking
notice, EPA views each facility as a separable SIP revision, and that
should it receive comment on one facility but not others, EPA may take
separate, final action on the remaining facilities.
---------------------------------------------------------------------------
\10\ While the commenter also references a ninth facility,
Montour, LLC, EPA is not acting on PADEP's CbC RACT II determination
for this facility at this time. As indicated in the proposed
rulemaking, EPA will be acting on sources located at this facility
in a separate future rulemaking.
---------------------------------------------------------------------------
Facilities with only VOC sources--The following facilities are
major source VOC emitting facilities that are minor sources of
NOX. As such, individual VOC sources at these facilities
must comply with RACT II requirements. EPA's approval in this
rulemaking for these facilities only relates to specific CbC VOC RACT
II determinations. EPA's approval of the Pennsylvania CbC VOC RACT II
SIP revisions for sources at these facilities does not involve
NOX emissions, maintains the status quo, and does not result
in an increase in VOC or NOX emissions. Therefore, as
explained previously, EPA has determined these SIP revisions will not
interfere with any applicable requirement concerning attainment and
reasonable further progress, or any other applicable requirement of the
CAA, pursuant to section 110(l).
Kovatch Mobile Equipment Corp
Letterkenny Army Depot
Volvo Construction Equipment North America
Facilities with VOC and NOX Sources (Only VOC CbC)--The following
facilities are major NOX and VOC emitting facilities, and
individual NOX and VOC sources at these facilities must
comply with RACT II requirements. However, EPA's approval in this
rulemaking for these facilities only relates to specific CbC VOC RACT
II determinations. EPA's approval of the Pennsylvania CbC VOC RACT II
SIP revisions for sources at these facilities does not involve any
NOX emissions, maintains the status quo, and does not result
in an increase in VOC or NOX emissions. Therefore, as
explained previously, EPA has determined these SIP revisions will not
interfere with any applicable requirement concerning attainment and
reasonable further progress, or any other applicable requirement of the
CAA, pursuant to section 110(l).
E.I DuPont de Nemours and Co.
National Fuel Gas Supply Corporation--Roystone Compressor
Station
Facilities with CbC NOX Sources--The following are major
NOX emitting sources and contain individual sources subject
to CbC NOX requirements that EPA is taking final action on
here. More specific information on those individual facilities follows:
Carmeuse Lime Inc.--EPA proposed to approve PADEP's RACT II CbC
NOX determination for one source at this facility. The other
NOX sources that were subject to RACT I are now shut down.
In its RACT II determination for Source 107 (No. 5 Kiln), PADEP
concluded that the use of a low NOX burner with good
combustion and burner optimization were technically and economically
feasible as RACT and were incorporated as part of the burner management
plan.\11\ Based on an analysis of historical performance testing data
from 2000 to 2017, the existing short-term emissions limit of 6.0 lbs
NOX/ton of lime produced was reduced to 4.6 lbs
NOX/ton of lime
[[Page 48912]]
produced as a RACT II case-by-case requirement. A burner management
plan, testing once every five years, and daily monitoring and
recordkeeping of fuel used hourly were also required. Through
imposition of this more stringent emission limit along with related
monitoring, testing, and recordkeeping requirements, Pennsylvania has
demonstrated that the status quo in NOX emissions has been
maintained, if not improved. As such EPA's approval of Pennsylvania's
SIP revision is adequately justified under section 110(l).
---------------------------------------------------------------------------
\11\ See PADEP's Technical Review Memo, dated November 19, 2018,
which is part of the docket for this rulemaking.
---------------------------------------------------------------------------
Merck, Sharpe & Dohme Corp.--EPA proposed to approve PADEP's RACT
II CbC NOX determination for two sources at this facility.
Numerous NOX sources that were subject to RACT I have been
shut down. In its determinations for the remaining two sources, PADEP
has determined that the RACT II CbC NOX is continued use of
low NOX burners and good operating practices and continued
compliance with the existing NOX emission limits.\12\
Through retention of the existing emission limits and continued use of
the low NOX burners, Pennsylvania has demonstrated that the
status quo in NOX emissions has been maintained. As such,
EPA's approval of Pennsylvania's SIP revision is adequately justified
under section 110(l).
---------------------------------------------------------------------------
\12\ See PADEP Revised Technical Review Memo, dated October 9,
2019, which is part of the docket for this rulemaking action.
---------------------------------------------------------------------------
Fairless Energy, LLC--EPA proposed to approve PADEP's RACT II
determination related to a NOX averaging plan for four
sources at this facility pursuant to 25 Pa. Code Sec. 129.98(a). The
averaging plan provision authorized in section 129.98 allows a facility
to establish an alternative facility-wide or system-wide RACT
NOX emissions limit as long as it demonstrates that the
resulting NOX emissions using a 30-day rolling average would
not be greater than NOX emissions from the group of included
sources if they each complied with the applicable presumptive
NOX RACT emissions limit as individual sources. Fairless
will be averaging the NOX emissions for four sources to meet
the RACT II requirements, an alternative emission limit, that will be
at least as stringent as the presumptive emission limit, which was
conditionally approved by EPA in a prior rulemaking.\13\ PADEP's
approval of the NOX averaging plan ensures that total
NOX emissions from these sources will be no greater than the
total individual emissions from each source if each were to comply with
the existing presumptive emission limit. The NOX averaging
plan also does not eliminate any other existing non-RACT emission
restrictions applicable to these sources. Through these measures,
Pennsylvania has demonstrated that the status quo in NOX
emissions has been maintained. As such, EPA's approval of PADEP's SIP
revision is adequately justified under section 110(l).
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\13\ See 84 FR 20274 (May 9, 2019) as to EPA's conditional
approval of the presumptive limit and PADEP's Technical Review Memo,
dated November 29, 2016, as to PADEP's analysis of the
NOX averaging plan.
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As described above, EPA determined that Pennsylvania had adequately
justified its RACT II CbC NOX determinations. EPA also
concluded, under section 110(l), that the status quo in NOX
emissions had been maintained, if not improved and that there is no
need to conduct the modeling suggested by the commenter. As noted
previously, the commenter included an air dispersion modeling analysis
of NOX emissions from a well pad at the Bighorn Pad Facility
in Colorado to highlight an alleged potential of NOX
emissions to cause or contribute to violations of the 2010 1-hour
NOX NAAQS. The NAAQS for nitrogen oxides is a 1-hour
standard at a level of 100 ppb based on the 3-year average of 98th
percentile of the yearly distribution of 1-hour daily maximum
NO2 concentrations. In 2012, EPA designated areas within
Pennsylvania as attainment/unclassifiable for the 2010 standard.\14\
The modeling analysis provided by the commenter indicated that
NOX emissions from the well pad area in Colorado could have
NO2 impacts within 50 kilometers of the source.
---------------------------------------------------------------------------
\14\ 77 FR 9532 (February 17, 2012).
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This modeling analysis from Colorado does not trigger a need for
EPA or Pennsylvania to conduct modeling on the impact of NOX
emissions from each individual PA CbC RACT source at issue in this
rulemaking in order for EPA to approve these SIP revisions. First, as
discussed previously, modeling is not the sole method available to
satisfy section 110(l) requirements. Second, the differences in the
meteorology, terrain, and facility configurations between the Bighorn
well pad and the Pennsylvania CbC RACT II sources are too significant
to rely on the Bighorn facility modeling results to serve as surrogate
modeling indicating that the Pennsylvania RACT II sources have the
potential to cause exceedances of the 2010 1-hour NOX NAAQS
in Pennsylvania. The commenter has not provided any comparison or
information to show why the Bighorn Pad Facility modeling results
should apply to these specific RACT II sources in Pennsylvania.
Further, the commenter has not presented any specific information
suggesting the RACT II CbC NOX determinations for these
specific sources could somehow lead to violations of the 2010 1-hour
NOX NAAQS. Without a more specific allegation from the
commenter about the sources in question, the commenter's allegations
are too speculative in nature to prevent EPA from approving PADEP's
RACT II CbC NOX determinations for sources at the eight
subject facilities.
Comment 2: The commenter is supportive of EPA's proposed
rulemaking, stating that it will positively affect citizens in the
Commonwealth of Pennsylvania for multiple reasons and has suggested
some editorial improvements for future rulemakings that could aid
citizen comprehension.
Response 2: EPA recognizes the commenter's support and suggestions.
EPA will consider such suggestions for future rulemakings.
Comment 3: The commenter states that the RACT limit for Carmeuse
Lime, Inc of 4.6 lb/NOX per ton of lime is too lenient.
Additionally, the commenter asserts the testing requirement to verify
the emissions limit by stack test once every five years is insufficient
and should have required a Continuous Emission Monitoring System (CEMS)
unit to monitor instantaneous emissions from the kiln or established an
emissions profile dependent on a number of factors that might impact
NOX emissions.
Response 3: As detailed in the facility files for Carmeuse Lime
contained in the docket for this action, the existing short-term
NOX limit for the No. 5 Kiln established under RACT I was
6.0 lbs NOX/ton of lime produced. The RACT II NOX
limit of 4.6 lb/ton approved here represents a reduction of emissions
from RACT I and was established through a statistical analysis using 17
years of historical performance testing data. PADEP also reviewed the
RACT/BACT/LAER Clearinghouse to determine emission limits for similar
kilns and found that such limits ranged from 3.59 to 9.98 lb/ton. Based
on this information included in the docket, EPA determined that the
NOX limit of 4.6 lb/ton comports with the CAA requirements
for RACT.
The requirement for stack testing every five years is consistent
with Pennsylvania's RACT II compliance demonstration requirements in 25
Pa. Code 129.100, which is a part of Pennsylvania's SIP-approved RACT
regulations. Under those regulations, a
[[Page 48913]]
five-year stack testing period for sources without a CEMS is
authorized. In addition to the stack testing, PADEP's RACT II
determination includes requirements for a burner management plan to
ensure good combustion and burner optimization. It also requires daily
recordkeeping on limestone used, lime produced, and fuel consumed to
provide a current picture of source operations.\15\ The sufficiency of
the stack testing requirement is further justified in light of a long
history of stack testing on this kiln, which produced the data that
enabled the lowering of the NOX limit. The RACT II
requirements for Kiln No. 5 are also consistent with the current
National Emission Standards for Hazardous Air Pollutants for Lime
Manufacturing Plants, 40 CFR 63, Subpart AAAAA, of which the source is
also subject. Given the basis of the emissions limit and the stack
testing requirement, plus the establishment of other burner and daily
recordkeeping requirements, EPA continues to find PADEP's analysis
reasonable and is finalizing the RACT determination for Carmeuse Lime.
---------------------------------------------------------------------------
\15\ See PADEP Technical Review Memo, dated November 19, 2018,
which is part of the docket for this rulemaking action.
---------------------------------------------------------------------------
Comment 4: The comment requests that EPA clarify which company is
subject to Permit No. 46-0005, included as part of EPA's proposed
rulemaking docket EPA-R03-OAR-2020-0597.
Response 4: Permit No. 46-0005 is the title V operating permit
number for Merck, Sharp, & Dohme Corp.'s facility located in West
Point, Upper Gwynedd Township, Montgomery County, Pennsylvania. The
cover page (page 1) of Permit No. 46-0005 contains additional owner,
plant, owner, and responsible official contact information for this
facility. Merck, Sharpe, and Dohme is the company name referred to in
the provisions to be incorporated into the SIP.
IV. Final Action
EPA is approving case-by-case RACT determinations and/or
alternative NOX emissions limits for eight sources in
Pennsylvania, as required to meet obligations pursuant to the 1997 and
2008 8-hour ozone NAAQS, as revisions to the Pennsylvania SIP.
V. Incorporation by Reference
In this document, EPA is finalizing regulatory text that includes
incorporation by reference. In accordance with requirements of 1 CFR
51.5, EPA is finalizing the incorporation by reference of source-
specific RACT determinations and alternative NOX emissions
limits under the 1997 and 2008 8-hour ozone NAAQS for certain major
sources of VOC and NOX in Pennsylvania. EPA has made, and
will continue to make, these materials generally available through
https://www.regulations.gov and at the EPA Region III Office (please
contact the person identified in the FOR FURTHER INFORMATION CONTACT
section of this preamble for more information). Therefore, these
materials have been approved by EPA for inclusion in the SIP, have been
incorporated by reference by EPA into that plan, are fully federally
enforceable under sections 110 and 113 of the CAA as of the effective
date of the final rule of EPA's approval, and will be incorporated by
reference in the next update to the SIP compilation.\16\
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\16\ 62 FR 27968 (May 22, 1997).
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VI. Statutory and Executive Order Reviews
A. General Requirements
Under the CAA, the Administrator is required to approve a SIP
submission that complies with the provisions of the CAA and applicable
Federal regulations. 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in
reviewing SIP submissions, EPA's role is to approve state choices,
provided that they meet the criteria of the CAA. Accordingly, this
action merely approves state law as meeting Federal requirements and
does not impose additional requirements beyond those imposed by state
law. For that reason, this action:
Is not a ``significant regulatory action'' subject to
review by the Office of Management and Budget under Executive Orders
12866 (58 FR 51735, October 4, 1993) and 13563 (76 FR 3821, January 21,
2011);
Does not impose an information collection burden under the
provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et seq.);
Is certified as not having a significant economic impact
on a substantial number of small entities under the Regulatory
Flexibility Act (5 U.S.C. 601 et seq.);
Does not contain any unfunded mandate or significantly or
uniquely affect small governments, as described in the Unfunded
Mandates Reform Act of 1995 (Pub. L. 104-4);
Does not have federalism implications as specified in
Executive Order 13132 (64 FR 43255, August 10, 1999);
Is not an economically significant regulatory action based
on health or safety risks subject to Executive Order 13045 (62 FR
19885, April 23, 1997);
Is not a significant regulatory action subject to
Executive Order 13211 (66 FR 28355, May 22, 2001);
Is not subject to requirements of section 12(d) of the
National Technology Transfer and Advancement Act of 1995 (15 U.S.C. 272
note) because application of those requirements would be inconsistent
with the CAA; and
Does not provide EPA with the discretionary authority to
address, as appropriate, disproportionate human health or environmental
effects, using practicable and legally permissible methods, under
Executive Order 12898 (59 FR 7629, February 16, 1994).
In addition, this rule does not have tribal implications as
specified by Executive Order 13175 (65 FR 67249, November 9, 2000),
because the SIP is not approved to apply in Indian country located in
the State, and EPA notes that it will not impose substantial direct
costs on tribal governments or preempt tribal law.
B. Submission to Congress and the Comptroller General
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report, which includes a copy of the rule,
to each House of the Congress and to the Comptroller General of the
United States. Section 804, however, exempts from section 801 the
following types of rules: Rules of particular applicability; rules
relating to agency management or personnel; and rules of agency
organization, procedure, or practice that do not substantially affect
the rights or obligations of non-agency parties. 5 U.S.C. 804(3).
Because this is a rule of particular applicability, EPA is not required
to submit a rule report regarding this action under section 801.
C. Petitions for Judicial Review
Under section 307(b)(1) of the CAA, petitions for judicial review
of this action must be filed in the United States Court of Appeals for
the appropriate circuit by November 1, 2021. Filing a petition for
reconsideration by the Administrator of this final rule does not affect
the finality of this action for the purposes of judicial review nor
does it extend the time within which a petition for judicial review may
be filed, and shall not postpone the effectiveness of such rule or
action. This action approving Pennsylvania's NOX and VOC
RACT requirements for eight facilities for the 1997 and 2008 8-hour
ozone NAAQS may not be challenged later in
[[Page 48914]]
proceedings to enforce its requirements. (See section 307(b)(2).)
List of Subjects in 40 CFR Part 52
Environmental protection, Air pollution control, Incorporation by
reference, Nitrogen dioxide, Ozone, Reporting and recordkeeping
requirements, Volatile organic compounds.
Dated: August 17, 2021.
Diana Esher,
Acting Regional Administrator, Region III.
For the reasons stated in the preamble, the EPA amends 40 CFR part
52 as follows:
PART 52--APPROVAL AND PROMULGATION OF IMPLEMENTATION PLANS
0
1. The authority citation for part 52 continues to read as follows:
Authority: 42 U.S.C. 7401 et seq.
Subpart NN--Pennsylvania
0
2. In Sec. 52.2020, the table in paragraph (d)(1) is amended by:
0
a. Revising the entries ``Merck and Co., Inc.--West Point Facility;''
``National Fuel Gas Supply Corp.--Roystone Compressor Station;'' and
``Department of the Army;'' and
0
b. Adding the following entries at the end of the table: ``Volvo
Construction Equipment North America;'' ``National Fuel Gas Supply
Corporation--Roystone Compressor Station;'' ``E.I. DuPont de Nemours
and Co.;'' ``Carmeuse Lime Inc.;'' ``Kovatch Mobile Equipment Corp.;''
``Merck, Sharpe & Dohme Corp. (formerly referenced as Merck and Co.,
Inc.--West Point Facility);'' ``Letterkenny Army Depot (formerly
referenced as Department of the Army);'' ``Fairless Energy, LLC.''
The revisions and additions read as follows:
Sec. 52.2020 Identification of plan.
* * * * *
(d) * * *
(1) * * *
--------------------------------------------------------------------------------------------------------------------------------------------------------
Additional explanations/Sec.
Name of source Permit No. County State effective EPA approval date Sec. 52.2063 and 52.2064
date citations \1\
--------------------------------------------------------------------------------------------------------------------------------------------------------
* * * * * * *
Merck and Co., Inc.--West Point OP-46-0005 Montgomery............ 1/13/97 6/23/00 4/18/01, 66 FR 19858. See also 52.2064(d)(6).
Facility.
* * * * * * *
National Fuel Gas Supply Corp.-- OP-62-141F Warren................ 4/1/03 10/27/04, 69 FR 62583 See also 52.2064(d)(2).
Roystone Compressor Station.
* * * * * * *
Department of the Army............. 28-02002 Franklin.............. 2/3/00 3/31/05, 70 FR 16416. See also 52.2064(d)(7).
* * * * * * *
Volvo Construction Equipment North 28-05012 Franklin.............. 6/1/19 9/1/21, [insert 52.2064(d)(1).
America. Federal Register
citation].
National Fuel Gas Supply 62-141H Warren................ 1/16/18 9/1/21, [insert 52.2064(d)(2).
Corporation--Roystone Compressor Federal Register
Station. citation].
E.I. DuPont de Nemours and Co...... 08-00002 Bradford.............. 9/28/18 9/1/21, [insert 52.2064(d)(3).
Federal Register
citation].
Carmeuse Lime Inc.................. 38-05003 Lebanon............... 3/6/19 9/1/21, [insert 52.2064(d)(4).
Federal Register
citation].
Kovatch Mobile Equipment Corp...... 13-00008 Carbon................ 10/27/17 9/1/21, [insert 52.2064(d)(5).
Federal Register
citation].
Merck, Sharpe & Dohme Corp. 46-00005 Montgomery............ 1/5/17 9/1/21, [insert 52.2064(d)(6).
(formerly referenced as Merck and Federal Register
Co., Inc.--West Point Facility). citation].
Letterkenny Army Depot (formerly 28-05002 Franklin.............. 6/1/18 9/1/21, [insert 52.2064(d)(7).
referenced as Department of the Federal Register
Army). citation].
Fairless Energy, LLC............... 09-00124 Bucks................. 12/6/16 9/1/21, [insert 52.2064(d)(8).
Federal Register
citation].
--------------------------------------------------------------------------------------------------------------------------------------------------------
* * * * *
0
3. Amend Sec. 52.2064 by adding paragraph (d) to read as follows:
Sec. 52.2064 EPA-Approved Source Specific Reasonably Available
Control Technology (RACT) for Volatile Organic Compounds (VOC) and
Oxides of Nitrogen (NOX).
* * * * *
(d) Approval of source-specific RACT requirements for 1997 and 2008
8-hour ozone national ambient air quality standards for the facilities
listed below are incorporated as specified below. (Rulemaking Docket
No. EPA-OAR-2020-0597).
(1) Volvo Construction Equipment North America, LLC.--Incorporating
by reference Permit No. 28-05012, effective June 1, 2019, as redacted
by Pennsylvania.
(2) National Fuel Gas Supply Corporation Roystone Compressor
Station--Incorporating by reference Permit No. 62-141H, effective
January 16, 2018, as redacted by Pennsylvania. All permit conditions in
the prior RACT Permit No. OP-62-141F, effective April 1, 2003, remain
as RACT requirements except for the Penneco boiler (1.5 MMBtu/hr) and
Struthers boiler (2.5 MMBtu/hr), which are no longer in operation. See
also Sec. 52.2063(c)(213)(i)(B)(1) for prior RACT approval.
(3) E.I. DuPont de Nemours and Company--Incorporating by reference
Permit No. 08-00002, effective September 28, 2018, as redacted by
Pennsylvania.
(4) Carmeuse Lime, Inc--Incorporating by reference Permit No. 38-
05003, effective March 6, 2019, as redacted by Pennsylvania.
(5) Kovatch Mobile Equipment Corporation--Incorporating by
reference Permit No. 13-00008, effective October 27, 2017, as redacted
by Pennsylvania.
(6) Merck, Sharp & Dohme Corporation--Incorporating by reference
Permit No. 46-00005, issued January 5, 2017, as redacted by
Pennsylvania, which supersedes the prior RACT Permit No. OP-46-0005,
issued January 13, 1997 and revised June 23, 2000, except for the
following conditions, which remain as a RACT requirements applicable to
the following sources:
[[Page 48915]]
Conditions #4A, #9C, and #13D for boiler 3 (Source ID 033); conditions
#4A, #9C, and #13D for boiler 5 (Source ID 035); conditions #4B and #9
for the gas turbine (Source ID 039); conditions #6A, #6B, and #6D for
any remaining shell freezers (Source ID 105); conditions #6A and #6D
for air emissions (disinfection; Source IDs 105, 107, 108, and 111);
conditions #4C and #9 for any remaining generators (various Source
IDs); condition #8 for research and development (Section C); and
condition #11 for any remaining deminimus sources (Section C). See also
Sec. 52.2063(c)(154)(i)(D) for prior RACT approval.
(7) Letterkenny Army Depot--Incorporating by reference Permit No.
28-05002, effective June 1, 2018, as redacted by Pennsylvania, which
supersedes the prior RACT Permit No. 28-02002, effective February 3,
2000 except for conditions 5, 6, 7, 8, 9, 10, 11, 12, and 14 which also
remain as RACT requirements. See also Sec. 52.2063(d)(1)(g) for prior
RACT approval.
(8) Fairless Energy, LLC--Incorporating by reference Permit No. 09-
00124, effective December 6, 2016 as redacted by Pennsylvania.
[FR Doc. 2021-18752 Filed 8-31-21; 8:45 am]
BILLING CODE 6560-50-P