Air Plan Approval; Pennsylvania; Reasonably Available Control Technology (RACT) Determinations for Case-by-Case Sources Under the 2008 8-Hour Ozone National Ambient Air Quality Standards, 60170-60178 [2021-22571]
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Federal Register / Vol. 86, No. 208 / Monday, November 1, 2021 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
section for
additional availability information.
FOR FURTHER INFORMATION CONTACT: Mr.
Riley Burger, Permits Branch (3AD10),
Air and Radiation Division, U.S.
Environmental Protection Agency,
Region III, 1650 Arch Street,
Philadelphia, Pennsylvania 19103. The
telephone number is (215) 814–2217.
Mr. Burger can also be reached via
electronic mail at burger.riley@epa.gov.
SUPPLEMENTARY INFORMATION:
INFORMATION CONTACT
40 CFR Part 52
[EPA–R03–OAR–2020–0598; FRL–9062–02–
R3]
Air Plan Approval; Pennsylvania;
Reasonably Available Control
Technology (RACT) Determinations for
Case-by-Case Sources Under the 2008
8-Hour Ozone National Ambient Air
Quality Standards
I. Background
Environmental Protection
Agency (EPA).
ACTION: Final rule.
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AGENCY:
On February 9, 2021, EPA published
a notice of proposed rulemaking
(NPRM). 86 FR 8743. In the NPRM, EPA
proposed approval of case-by-case
SUMMARY: The Environmental Protection
RACT determinations or alternative
Agency (EPA) is approving multiple
NOX emissions limits for sources at nine
state implementation plan (SIP)
facilities in Philadelphia County, as
revisions submitted by the
EPA found that the RACT controls for
Commonwealth of Pennsylvania. These
these sources met the CAA RACT
revisions were submitted by the
requirements for the 2008 8-hour ozone
Pennsylvania Department of
NAAQS. PADEP, on behalf of
Environmental Protection (PADEP) to
Philadelphia Air Management Services
establish and require reasonably
(AMS), submitted the SIP revisions for
available control technology (RACT) for sources at these facilities on May 7,
individual major sources of volatile
2020.
organic compounds (VOC) and nitrogen
Under certain circumstances, states
oxides (NOX) pursuant to the
are required to submit SIP revisions to
Commonwealth of Pennsylvania’s
address RACT requirements for both
conditionally approved RACT
major sources of NOX and VOC and any
regulations. In this rule action, EPA is
source covered by control technique
approving source-specific RACT
guidelines (CTG) for each ozone
determinations (‘‘case-by-case’’ or
NAAQS. Which NOX and VOC sources
alternative NOX emissions limits) for
in Pennsylvania are considered ‘‘major,’’
sources at nine major NOX and VOC
and are therefore subject to RACT, is
emitting facilities located in
dependent on the location of each
Philadelphia County. These RACT
source within the Commonwealth.
evaluations were submitted to meet
Sources located in nonattainment areas
RACT requirements for the 2008 8-hour would be subject to the ‘‘major source’’
ozone national ambient air quality
definitions established under the CAA
standard (NAAQS). EPA is approving
based on the area’s current
these revisions to the Pennsylvania SIP
classification(s). In Pennsylvania,
in accordance with the requirements of
sources located in any ozone
the Clean Air Act (CAA) and EPA’s
nonattainment areas outside of
implementing regulations.
moderate or above are subject to source
DATES: This final rule is effective on
thresholds of 50 tons per year (tpy)
December 1, 2021.
because of the Ozone Transport Region
ADDRESSES: EPA has established a
(OTR) requirements in CAA section
docket for this action under Docket ID
184(b)(2).
On May 16, 2016, PADEP submitted
Number EPA–R03–OAR–2020–0598. All
a SIP revision addressing RACT for both
documents in the docket are listed on
the 1997 and 2008 8-hour ozone
the https://www.regulations.gov
NAAQS in Pennsylvania. PADEP’s May
website. Although listed in the index,
16, 2016 SIP revision intended to
some information is not publicly
address certain outstanding non-CTG
available, e.g., confidential business
VOC RACT, VOC CTG RACT, and major
information (CBI) or other information
whose disclosure is restricted by statute. source VOC and NOX RACT
Certain other material, such as
requirements for both standards. The
copyrighted material, is not placed on
SIP revision requested approval of
the internet and will be publicly
Pennsylvania’s 25 Pa. Code 129.96–100,
available only in hard copy form.
Additional RACT Requirements for
Publicly available docket materials are
Major Sources of NOX and VOCs (the
available through https://
‘‘presumptive’’ RACT II rule). Prior to
www.regulations.gov, or please contact
the adoption of the RACT II rule,
the person identified in the FOR FURTHER Pennsylvania relied on the NOX and
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VOC control measures in 25 Pa. Code
129.92–95, Stationary Sources of NOX
and VOCs, (the RACT I rule) to meet
RACT for non-CTG major VOC sources
and major NOX sources. The
requirements of the RACT I rule remain
as previously approved in
Pennsylvania’s SIP and continue to be
implemented as RACT.1 On September
26, 2017, PADEP submitted a letter,
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 letter.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 plan 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 (i.e., by 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 NOX
averaging plan limits. This rule is based
on EPA’s review of one of these SIP
submissions.
The SIP revisions in this action only
establish 2008 8-hour ozone NAAQS
RACT requirements. Applicable RACT
requirements under the CAA for sources
located in Philadelphia for the 1997 8hour ozone NAAQS were previously
satisfied. See 81 FR 69687 (October 7,
2016).
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 NOX averaging plan limits
and/or case-by-case RACT requirements
for major sources in Pennsylvania
1 The RACT I Rule was approved by EPA into the
Pennsylvania SIP on March 23, 1998. 63 FR 13789.
Through this rule, certain source-specific RACT I
requirements will be superseded by more stringent
requirements. See Section II of this preamble.
2 On August 27, 2020, the Third Circuit Court of
Appeals vacated three provisions of Pennsylvania’s
presumptive RACT II rule applicable to certain
coal-fired power plants. Sierra Club v. EPA, No. 19–
2562 (3rd Cir. August 27, 2020). None of the sources
in this rule are subject to the presumptive RACT II
provisions at issue in the Sierra Club decision.
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subject to 25 Pa. Code 129.98 or 129.99.
Among the Pennsylvania SIP revisions
submitted by PADEP were case-by-case
RACT determinations and alternative
NOX emissions limits for certain sources
in Philadelphia County, which PADEP
submitted on behalf of AMS. PADEP’s
submission included SIP revisions
pertaining to source-specific RACT
requirements for the existing emissions
units at each of the major sources of
NOX and/or VOC that required a sourcespecific RACT determination or
alternative NOX emissions limits for
major sources seeking such limits.
In the case-by-case RACT
determinations submitted by PADEP on
behalf of AMS, an evaluation was
completed to determine if previously
SIP-approved, case-by-case RACT
emissions limits or operational controls
were more stringent than the new RACT
II presumptive or case-by-case
requirements. If more stringent, the
previously approved RACT
requirements will continue to apply to
the applicable source and are included
in the new RACT II permit. If the new
case-by-case RACT II requirements are
more stringent than the previously
approved RACT requirements, then the
RACT II requirements will supersede
the prior RACT requirements.3
In AMS’ RACT determinations
involving NOX averaging, an evaluation
was completed to determine that the
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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 approving SIP revisions
pertaining to case-by-case RACT
requirements and alternative NOX
emissions limits for sources at nine
major NOX and/or VOC emitting
facilities in Philadelphia County, as
summarized in Table 1 in this
document.
TABLE 1—NINE MAJOR NOX AND/OR VOC EMITTING FACILITIES IN PENNSYLVANIA SUBJECT TO SOURCE-SPECIFIC RACT
II DETERMINATIONS UNDER THE 2008 8-HOUR OZONE NAAQS
Major source
(county)
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AdvanSix Resins & Chemicals LLC—Frankford Plant (formerly Honeywell
International—Frankford Plant).
Exelon Generation Company—Richmond Generating Station .......................
Grays Ferry Cogeneration Partnership—Schuylkill Station .............................
Vicinity Energy Philadelphia—Schuylkill Station (formerly Veolia Energy
Philadelphia—Schuylkill Station).
Kinder Morgan Liquids Terminals, LLC—Philadelphia Terminal .....................
Naval Surface Warfare Center—Philadelphia Division formerly Naval Surface Warfare Center—Carderock Division, Ship Systems Engineering Station).
Newman and Company, Inc (formerly Paperworks Industries, Inc) ................
Philadelphia Energy Solutions Refining and Marketing LLC ...........................
Philadelphia Shipyard Inc ................................................................................
1997 8-hour
ozone RACT
source?
(RACT I)
Major source
pollutant
(NOX and/or VOC)
Yes ...............
NOX and VOC .......
IP16–000276 (3/5/2020).
Yes ...............
Yes ...............
Yes ...............
NOX ........................
NOX ........................
NOX ........................
IP16–000246 (4/20/2020).
IP–16–000250 (3/4/2020).
IP16–000249 (3/4/2020).
Yes ...............
Yes ...............
VOC .......................
NOX ........................
IP16–000233 (4/20/2020).
IP16–000235 (3/20/2020).
Yes ...............
Yes ...............
No ................
NOX ........................
NOX and VOC .......
VOC .......................
IP–000223 (3/31/2020).
IP–16–00269 (4/24/2020).
IP16–000300 (4/8/2020).
The case-by-case RACT
determinations submitted by PADEP, on
behalf of AMS, consist of an evaluation
of all reasonably available controls at
the time of evaluation for each affected
emissions unit, resulting in an AMS
determination of what specific
emissions limit or control measures
satisfy RACT for that particular unit.
The adoption of new, additional, or
revised emissions 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 AMS to the source.
Similarly, AMS’ 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 into 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 of this preamble,
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–2019–0657.4 EPA is
incorporating by reference in the
Pennsylvania SIP, via the RACT II
permits, source-specific RACT
emissions limits and control measures
and alternative NOX emissions limits
under the 2008 8-hour ozone NAAQS
for certain major sources of NOX and
VOC emissions.
3 While the prior SIP-approved RACT permit will
remain part of the SIP, this RACT II rule will
incorporate by reference the RACT II requirements
through the RACT II permit, which will also
contain any more stringent requirements from the
previously approved RACT permit.
4 The RACT II permits included in the docket for
this rule are redacted versions of the facilities’
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B. EPA’s Final Action
PADEP’s SIP revisions incorporate
AMS’ determinations of source-specific
RACT II controls for individual
emission units at major sources of NOX
and/or VOC in Philadelphia, where
those units are not covered by or cannot
meet Pennsylvania’s presumptive RACT
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RACT II permit
(effective date)
regulation or where included in a NOX
averaging plan. After thorough review
and evaluation of the information
provided by AMS in the SIP revision
submittals for sources at nine major
NOX and/or VOC emitting facilities in
Philadelphia, EPA found that: (1) AMS’
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) AMS’
determinations on alternative NOX
emissions 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) AMS’ determinations are
consistent with the CAA, EPA
regulations, and applicable EPA
guidance.
federally enforceable permits. They reflect the
specific RACT requirements being approved into
the Pennsylvania SIP via this final action.
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AMS, in its RACT II determinations,
considered the prior source-specific
RACT requirements and, where more
stringent, retained those prior RACT
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 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 the NAAQS,
reasonable further progress, or other
applicable requirements under section
110(l) of the CAA.
Other specific requirements of the
2008 8-hour ozone NAAQS case-by-case
RACT determinations and alternative
NOX emissions limits and the rationale
for EPA’s proposed action are explained
more thoroughly in the NPRM, and its
associated technical support document
(TSD), and will not be restated here.
III. EPA’s Response to Comments
Received
EPA received comments from three
commenters on the February 9, 2021
NPRM. 86 FR 8743. 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 2008 8hour 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 NAAQS 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
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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 and allow for comment on any
such modeling information or other
information utilized in the
demonstration that the NAAQS will be
protected.5
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
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. For
subject sources located in Philadelphia,
the City of Philadelphia’s AMS is the
government agency responsible for
making such determinations.
As required by Pennsylvania’s RACT
II regulations, AMS then conducted, for
sources seeking a CbC determination, an
analysis examining what air pollution
controls were available for those
individual sources to determine the
lowest emissions 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 For sources seeking an
alternative NOX emissions limit, AMS
reviewed the NOX averaging plan to
determine that the alternative NOX
emissions limits demonstrated that the
emissions under the averaging plan
were equivalent to emissions as if the
individual sources were operating in
accordance with the applicable
presumptive limit.
5 This summary of the comment includes
supplemental information provided by the
commenter in a similar comment to EPA’s proposed
rulemaking in EPA–R03–OAR–2020–0597.
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).
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Through its source-specific RACT II
determinations, AMS has established
NOX and VOC limits and requirements
for various sources that either reaffirm
existing emissions limits or makes the
limits more stringent. PADEP, on behalf
of AMS, 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 nine facilities in Philadelphia
County. 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. For these reasons, EPA
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 RACT II 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
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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);
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. In both cases, the
state 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. In both Kentucky
Resources and Indiana, the court
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. 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
Guardians 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 Guardians 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 Guardians
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, AMS is
9 759
F.3d at 1074.
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not relaxing standards or eliminating a
program; rather, AMS is only reevaluating the technical and economic
feasibility of air pollution controls for
subject air pollution sources as required
by implementation of the 2008 8-hour
NAAQS. Based on that review, AMS, as
explained in more detail below, has
made determinations that either retain
or make more stringent existing NOX
emissions limits. Emissions are not
expected to increase, and will likely
decrease, as a result of AMS’ RACT II
NOX CbC determinations and EPA’s
approval hereof. Under these
circumstances, AMS’ demonstration to
meet the requirements of section 110(l)
for its source-specific 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 source-specific NOX RACT
determinations are preserving the status
quo air quality or achieving additional
reductions beyond the status quo.
With this rule action, EPA is only
approving revisions that add specific
NOX and VOC source-specific RACT II
determinations to the Pennsylvania SIP.
In the subject RACT II source-specific
determinations, AMS has made an
adequate showing that its sourcespecific determinations for individual
sources at the nine 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
memoranda and related documents,
which are included in the docket for
this rule, AMS evaluated both the
technical and economic feasibility of
various control equipment for these
sources and used that evaluation to
determine the RACT II requirements.
AMS 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 40 CFR part 51,
appendix V. The record supporting
EPA’s approval of AMS’ source-specific
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.
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The facilities in this rule identified as
objectionable in the comment break
down into the categories listed below.
As explained in the proposed
rulemaking document, 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—
Kinder Morgan Liquid Terminals, LLC
is a major source VOC emitting facility
that is a minor source of NOX. As such,
individual VOC sources at this facility
must comply with RACT II
requirements. EPA’s approval in this
rule for this facility only relates to
specific CbC VOC RACT II
determinations. EPA’s approval of the
Pennsylvania CbC RACT II SIP revision
for sources at for this facility does not
involve NOX emissions, maintains the
status quo in VOC emissions, and does
not result in an increase in VOC or NOX
emissions. Therefore, as explained
previously, EPA has determined this SIP
revision will not interfere with any
applicable requirement concerning
attainment, reasonable further progress,
or any other applicable requirement of
the CAA pursuant to section 110(l).
Facilities with CbC NOX Sources—
The following facilities 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:
Exelon Generation Company—
Richmond Generating Station—EPA
proposed to approve AMS’ RACT II CbC
NOX determination for two combustion
turbines at this facility. After
determining that there were no new
technically and economically feasible
NOX controls for these sources, AMS
has determined that the RACT II NOX is
continuing to comply with the existing
NOX emissions limits and capacity
factor.10 Through retention of the
existing emissions limits and
restrictions, AMS has demonstrated that
the status quo in NOX emissions has
been maintained. As such, EPA’s
approval of the Pennsylvania SIP
revision for the individual sources at
this facility is adequately justified under
section 110(l).
Grays Ferry Cogeneration
Partnership—Schuylkill Station (GFCP)
and Vicinity Energy Philadelphia—
Schuylkill Station (Vicinity)—The two
facilities hold separate operating
permits, but they share a geographic
10 See AMS’ InterOffice Memo, dated April 20,
2020, which is part of the docket for this rule.
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location and are considered a single
source for title V and New Source
Review purposes. EPA proposed to
approve AMS’ RACT II determination
related to a facility-wide NOX averaging
plan for three 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 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.
GFCP and Vicinity will be averaging the
NOX emissions for three sources to meet
the RACT II requirements, an alternative
emissions limit, that will be at least as
stringent as the presumptive emissions
limits, which were conditionally
approved by EPA in a prior rule.
Additionally, AMS has retained all of
the individual emissions limits from the
prior RACT approval.11 AMS’ approval
of the alternative NOX emissions limit
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 emissions limit.
The alternative NOX emissions limit
does not eliminate the prior individual
emissions limits. Through these
measures, AMS has demonstrated that
the status quo for NOX emissions has
been maintained. As such, EPA’s
approval of the Pennsylvania SIP
revision for the individual sources at
these facilities is adequately justified
under section 110(l).
Philadelphia Energy Solutions
Refining and Marketing LLC (PES)—EPA
proposed to approve AMS’ RACT II CbC
NOX determinations for numerous
sources at this facility and its alternative
NOX emissions limits for a number of
heaters and boilers. At the time AMS
issued the current RACT Plan Approval
to PES in April 2020, which
incorporated its RACT II NOX
determinations, refining operations at
the PES facility had been shut down.
The refinery has been closed since June
2019, and the facility has been sold to
a new owner. AMS’ proposed RACT II
SIP revision does not authorize new
operations at the facility, but rather
incorporates RACT requirements for
major NOX and VOC sources in
operation as of 2012 into the SIP.
For the CbC NOX sources at the
facility, AMS has determined that all
proposed 2008 NOX RACT requirements
(such as emissions limits, control
technologies like selective catalytic
reduction (SCR) and low NOX burners,
continuous emissions monitoring
systems (CEMs), combustion tuning,
and good combustion practices), are at
least as stringent as the prior 1997 8hour NOX RACT requirements and has
included them in the new 2020 RACT
permit, which will be incorporated into
the Pennsylvania SIP through this
action. At the same time, AMS also
approved for a group of heaters and
boilers alternative NOX emissions limits
through the use of three NOX averaging
plans 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 NOX emissions limit as
long as it demonstrates that the resulting
NOX emissions using a 30-day rolling
average would not be greater than the
NOX emissions from the group of
included sources if they each complied
with the applicable presumptive NOX
RACT emissions limit as individual
sources. The facility is required to
average the NOX emissions for three
groups of sources to meet the RACT II
requirements, an alternative emissions
limit, that will be at least as stringent as
the presumptive emissions limit, which
was conditionally approved by EPA in
a prior rule.12
Through retention of the existing
emissions limits and the approval of the
alternative NOX emissions limits at the
facility, AMS has demonstrated that the
status quo in NOX emissions has been
maintained. As such, EPA’s approval of
the Pennsylvania SIP revision for the
individual sources at this facility is
adequately justified under section
110(l).
As described above, EPA determined
that AMS adequately justified its RACT
II CbC NOX determinations and
alternative NOX emissions limits. 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-
11 See 84 FR 20274 (May 9, 2019) as to EPA’s
conditional approval of the presumptive limit and
AMS’ Inter Office Memo, dated March 4, 2020,
which is part of the docket for this rule.
12 See 84 FR 20274 (May 9, 2019) as to EPA’s
conditional approval of the presumptive limit and
AMS’ Inter Office Memo, dated April 24, 2020,
which is part of the docket for this rule.
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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.13 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 data analysis from
Colorado does not trigger a need for
EPA, Pennsylvania, or AMS to conduct
modeling on the impact of NOX
emissions from each individual source
at issue in this rule 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 Philadelphia
RACT II sources are too significant to
rely on the Bighorn facility modeling
results to serve as surrogate modeling
indicating that the Philadelphia 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 Philadelphia.
Further, the commenter has not
presented any specific information
suggesting the RACT II CbC NOX
determinations or alternative NOX
emissions limits 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 AMS’
RACT II CbC NOX determinations or
alternative NOX emissions limits for
sources at the five subject facilities.
Comment 2: The commenter states
that minor errors are present in the
technical and economic feasibility
analysis of available controls throughout
the proposed rulemaking. The
commenter asserts that in several
instances, the discussion of costs
incorrectly led to the conclusion that
certain controls were technically
infeasible, rather than identifying those
controls as technically feasible and then
evaluating the cost issues in the
economic analysis. The specific
13 77
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instances in which commenter claims
there are minor errors are in the
evaluation of a fuel switch to natural
gas, water/steam injection, and SCR for
boilers.
The commenter also raises concern
with the use, in the economic feasibility
analysis, of outdated interest rates that
are not reflective of current economic
conditions and the consumer price
index (CPI) to adjust air pollution
control costs to current dollar values.
Ultimately, the commenter
acknowledges that if the RACT
evaluations were redone in a manner to
address the identified concerns, the
control technologies determined to be
RACT would not change.
Response 2: The commenter correctly
asserts that an evaluation of the
technical feasibility of available controls
should be conducted before evaluating
the economic feasibility of the
remaining available controls. 25 Pa.
Code 129.92(b) and 129.99(d)(1). The
TSD, which is included in the docket
file for this action, explains the basis for
EPA’s approval of the RACT
determinations included in this rule.
From its review of the specific RACT
determinations made by AMS in this
rule, EPA cannot locate a source where
there was a determination where water/
steam injection was identified as
technically infeasible. Similarly, except
for two heaters at the PES facility, there
are no determinations where SCR on a
boiler was identified as technically
infeasible. For the two exceptions,
Heaters 860–2H8 and 864–PH7, SCR
was determined to be infeasible because
of physical space constraints, not due to
the use of ammonia or urea as identified
by the commenter.
As to the commenter’s remarks about
fuel switching, it appears that they may
apply to the Exelon Generating
Company—Richmond Station where a
fuel switch to natural gas was
determined to be technically infeasible
for Combustion Turbine #91 and #92. In
this instance, Exelon identified the
large-scale costs and related regulatory
requirements as technical impediments
to installing a natural gas line to the
facility, and AMS agreed with this
analysis and determined that it was not
technically feasible. Whether or not
AMS’ conclusion on the technical
feasibility analysis was sufficient does
not change the final conclusion on the
overall feasibility of the potential use of
fuel switching for the sources at this
facility. EPA agrees with the commenter
that determining fuel switching as a
technically feasible control would not
change the determination that this
control is ultimately infeasible as RACT
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for the sources at hand and is finalizing
AMS’ proposed RACT requirements.
EPA also agrees with the commenter
that choosing suitable interest rates and
cost escalation factors is a requirement
of RACT determinations. Per 25 Pa.
Code 129.92(b)(4), the cost effectiveness
evaluation must be consistent with the
OAQPS Control Cost Manual (Fourth
Edition) EPA 450/3–90–006 January
1990 (Control Cost Manual) and
subsequent revisions.14 The Control
Cost Manual addresses appropriate use
of the CPI and lays out general
principals to make accurate escalation
calculations and choose appropriate
interests rates. However, the Control
Cost Manual in its current form does not
specifically prohibit use of the CPI.
The commenter did not specify which
economic feasibility determinations in
this rule contain questionable interest
rates or cost escalations but recognizes
that updates to such factors in the
economic analysis would not
necessarily change the final RACT
determinations. These factors are among
many other values used in a complex,
multi-factor cost analysis. EPA agrees it
is not clear that revised interest rate or
cost escalations in the economic
analysis would change the final
conclusions of the determinations
contained in this rule. Without a more
specific allegation from the commenter
about the sources in question, the
commenter’s allegations are too general
and speculative in nature to prevent
EPA from approving AMS’ RACT II CbC
determinations for sources at the nine
subject facilities.
Comment 3: The commenter raises
concern with the Grays Ferry
Cogeneration Partnership and Vicinity
Energy NOX averaging plan and the
Philadelphia Energy Solutions Refining
and Marketing LLC (PES) NOX averaging
plan. Specifically the commenter
asserts: (1) In order to be protective of
the 8-hour average of the 2008 ozone
NAAQS, particularly during ozone
season, these RACT determinations
should include short term emissions
limits on a calendar day basis (as is
done in New Jersey and other states),
rather than a 30 operating day rolling
average; (2) Grays Ferry Cogeneration
Partnership and Vicinity Energy should
be required to evaluate control options
of combusting only natural gas,
replacing No. 6 oil with No. 2 oil, and
additional NOX controls; and (3) due to
the recent events at PES, including
shutting down operations, bankruptcy,
14 The OAQPS Control Cost Manual referenced in
25 Pa. Code 129.92(b)(4) is also known as the EPA
Air Pollution Control Cost Manual. OAQPS is the
acronym for EPA’s Office of Air Quality Planning
and Standards.
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60175
and sale, EPA should not approve the
proposed SIP revision until a new
owner begins operations at the facility.
More generally, the commenter asserts
that EPA should establish term limits
for RACT plan approvals and ensure
that facilities re-evaluate RACT plans to
incorporate any future advancements in
technology as is required by New Jersey
RACT rules.
Response 3: In its conditional
approval of Pennsylvania’s overall
RACT II program at 25 Pa. Code 129.96–
129.100 (84 FR 20274, May 9, 2019),
EPA explained that under 25 Pa. Code
129.98, affected major sources unable to
meet the applicable presumptive RACT
emissions limitation may choose to
comply with alternative NOX
requirements based on averaging NOX
emissions from multiple sources.
Specifically, EPA explained that
averaging plans pursuant to
Pennsylvania’s RACT II regulations are
intended to demonstrate 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. Thus, the use of
a 30-day rolling average for NOX
averaging plans under Pennsylvania’s
RACT II program was previously
approved by EPA.
EPA guidance does highlight the need
for emission controls that are reasonably
consistent with protecting a short-term
NAAQS such as ozone. However, in
those cases where an emissions limit for
a RACT control can be quantified, EPA
guidance states that averaging periods
for such limits should be as short as
practicable and in no case longer than
30 days. See the January 20, 1984 EPA
guidance memorandum titled
‘‘Averaging Times for Compliance with
VOC Emissions Limits—SIP Revision
Policy.’’
In the instance of Grays Ferry
Cogeneration Partnership and Vicinity
Energy, the facilities are using an
averaging plan to limit NOX emissions
from the combustion turbine, Boiler
#25, and Boiler #26 to no greater than
the NOX emissions that would have
resulted had each individual source
complied with the presumptive RACT
limits of 25 Pa. Code 129.97(g)(2)(i)(A)
and (B) and 129.97(g)(1)(i) and (ii). PES
is using averaging plans to limit
emissions from Heaters 137 F–1, 137 F–
2, 137 F–3, 1332 H–400, and 1332 H–
401 and #3 Boilerhouse Boilers #37,
#39, and #40 to no greater than the NOX
emissions that would have resulted had
each individual source complied with
the presumptive RACT limits of 25 Pa.
Code 129.97(g)(1)(iv). In each instance,
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the 30-day rolling average used for
demonstrating compliance is consistent
with the requirements contained in
Pennsylvania’s previously approved
RACT II program.
EPA disagrees with the commenter
that Grays Ferry Cogeneration
Partnership and Vicinity Energy should
evaluate the technical and economic
feasibility of certain alternative control
options. The evaluation of alternative
controls is only a requirement for
sources opting for case-by-case RACT
evaluation under 25 Pa. Code 129.99.
Sources at the subject facilities are
complying with RACT through the NOX
emission averaging plan provisions
under 25 Pa. Code 129.98. Accordingly,
they are not required to evaluate
potential alternative control options as
required by the case-by-case option.
EPA also disagrees with the
commenter’s recommendation to
disapprove the NOX averaging plan for
the PES facility and wait for action by
a new owner. EPA acknowledges the
commenter’s references to the shutdown
of refining operations at the PES facility
in June 2019, the subsequent
bankruptcy filing by PES, and the
prospective sale of the facility.
Nevertheless, Pennsylvania’s RACT II
requirements apply to major NOX and
VOC emitting facilities that were in
existence on or before July 20, 2012. 25
Pa. Code 129.96. Proposed NOX
averaging plans were required to be
submitted to the government by October
24, 2016. 25 Pa. Code 129.98. As AMS’
approval of the NOX averaging plans for
certain sources at PES was submitted to
EPA as a SIP revision, meets the
requirements of Pennsylvania’s RACT II
NOX averaging provisions, and has not
been withdrawn, EPA is finalizing the
proposed RACT II requirements for
those sources.
Finally, EPA declines to establish
term limits for RACT plan approvals to
ensure the periodic re-evaluation of
technologies as required by New Jersey’s
RACT rules. The Clean Air Act and the
requirements to implement RACT are
designed to protect public health and
the environment. However, the only
factors EPA is legally required to
consider for approving RACT are those
in the statute, EPA’s regulations, and the
SIP-approved Pennsylvania
implementing regulations. Term limits
for RACT plan approvals for periodic reevaluation of technologies is not a
statutory or regulatory requirement for
approval of these RACT determinations.
Even without such term limits, RACT is
periodically reevaluated in nonattainment areas after the promulgation
of a new ozone NAAQS.
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IV. Final Action
EPA is approving the case-by-case
RACT determinations and/or alternative
NOX emissions limits for sources at nine
major NOX and VOC emitting facilities
in Philadelphia, as required to meet
obligations pursuant to the 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 NOX averaging plan
limits under the 2008 8-hour ozone
NAAQS for certain major sources of
VOC and NOX in Philadelphia County.
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.15
V. 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
15 62
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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 nonagency parties. 5 U.S.C. 804(3). Because
this is a rule of particular applicability,
EPA is not required to submit a rule
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Dated: October 8, 2021.
Diana Esher,
Regional Administrator, Region III.
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 January 3, 2022. 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 nine facilities
for 2008 8-hour ozone NAAQS may not
be challenged later in 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.
Name of source
PART 52—APPROVAL AND
PROMULGATION OF
IMPLEMENTATION PLANS
1. The authority citation for part 52
continues to read as follows:
■
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 ‘‘Exelon
Generation Company—Richmond
Generating Station’’; ‘‘Grays Ferry
Cogeneration Partnership—Schuylkill
Station’’; ‘‘Honeywell International—
Frankford Plant’’; ‘‘Kinder Morgan
Liquid Terminals, LLC’’; ‘‘Naval Surface
Warfare Center—Carderock Division,
Ship Systems Engineering Station
(NSWCCD–SSES)’’; ‘‘Paperworks
Industries, Inc’’; ‘‘Philadelphia Energy
Solutions—Refining and Marketing,
LLC’’; and ‘‘Veolia Energy
Philadelphia—Schuylkill Station’’;
■ b. Adding entries at the end of the
table for ‘‘AdvanSix Resins & Chemicals
■
Permit No.
*
*
Exelon Generation Company—Richmond
Generating Station.
Grays Ferry Cogeneration Partnership—
Schuylkill Station.
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For the reasons set out in the
preamble, 40 CFR part 52 is amended as
follows:
State
effective
date
County
§ 52.2020
*
*
*
Supersedes previously approved RACT
permit. See also 52.2064(f)(2).
Source is aggregated with Veolia Energy
Efficiency, LLC and Veolia Energy—
Schuylkill
Station.
See
also
52.2064(f)(3).
Supersedes previously approved RACT
permit. Source was formerly Sunoco
Chemicals, Frankford Plant. See also
52.2064(f)(1).
Supersedes previously approved RACT
permit. Source was formerly GATX Terminal
Corporation.
See
also
52.2064(f)(5).
Supersedes previously approved RACT
permits. Source was formerly U.S.
Navy, Naval Surface Warfare Center,
Carderock Division (NSWCCD). See
also 52.2064(f)(6).
Supersedes previously approved RACT
permit. Source was formerly Jefferson
Smurfit, Corp./Container Corp. of America. See also 52.2064(f)(7).
Supersedes previously approved RACT
permit. Source was formerly Sunoco
Inc. (R&M)—Philadelphia. See also
52.2064(f)(8).
PA–51–4944 ...
Philadelphia ....
1/09/15
10/7/16, 81 FR 69691 ....
Honeywell International—Frankford Plant
PA–51–1151 ...
Philadelphia ....
02/09/16
10/07/16, 81 FR 69691 ..
Kinder Morgan Liquid Terminals, LLC .......
PA–51–5003 ...
Philadelphia ....
02/09/16
10/7/16, 81 FR 69691 ....
Naval
Surface
Warfare
Center—
Carderock Division, Ship Systems Engineering Station (NSWCCD–SSES).
PA–51–9724 ...
Philadelphia ....
02/09/16
10/7/16, 81 FR 69691 ....
Paperworks Industries, Inc ........................
PA–51–1566 ...
Philadelphia ....
1/09/15
10/7/16, 81 FR 69691 ....
Philadelphia Energy Solutions—Refining
and Marketing, LLC.
PA–51–01501;
PA–51–
01517.
Philadelphia ....
02/09/16
10/7/2016, 81 FR 69691
02/09/16
*
10/7/16, 81 FR 69691 ....
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*
Philadelphia ....
Frm 00019
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*
Additional explanations/§§ 52.2063 and
52.2064 citations 1
*
10/07/16, 81 FR 69691 ..
*
*
EPA approval date
02/09/16
PA–51–4942 ...
Identification of plan.
*
*
(d) * * *
(1) * * *
Philadelphia ....
*
*
Philadelphia—Schuylkill
*
LLC—Frankford Plant (formerly
referenced as Honeywell International—
Frankford Plant)’’; ‘‘Vicinity Energy
Philadelphia—Schuylkill Station
(formerly referenced as Veolia Energy
Philadelphia—Schuylkill Station)’’;
‘‘Kinder Morgan Liquid Terminals,
LLC—Philadelphia Terminal (formerly
referenced as Kinder Morgan Liquid
Terminals, LLC)’’; ‘‘Naval Surface
Warfare Center—Philadelphia Division
(formerly referenced as Naval Surface
Warfare Center—Carderock Division,
Ship Systems Engineering Station)
(NSWCCD–SSES))’’; ‘‘Newman and
Company, Inc (formerly referenced as
Paperworks Industries, Inc)’’;
‘‘Philadelphia Energy Solutions
Refining and Marketing LLC (formerly
referenced as Philadelphia Energy
Solutions—Refining and Marketing,
LLC)’’; and ‘‘Philadelphia Shipyard
Inc.’’; and
■ c. Adding additional entries at the end
of the table for ‘‘Exelon Generation
Company—Richmond Generating
Station’’ and ‘‘Grays Ferry Cogeneration
Partnership—Schuylkill Station’’.
The revisions and additions read as
follows:
PA–51–4903 ...
Veolia Energy
Station.
*
60177
E:\FR\FM\01NOR1.SGM
*
*
Supersedes previously approved RACT
permit. Source was formerly TRIGEN—
Schuylkill Station. Source is aggregated
with Grays Ferry Cogeneration Partnership and Veolia Energy Efficiency, LLC.
See also 52.2064(f)(4).
01NOR1
60178
Federal Register / Vol. 86, No. 208 / Monday, November 1, 2021 / Rules and Regulations
Name of source
Permit No.
*
*
AdvanSix Resins & Chemicals LLC—
Frankford Plant (formerly referenced as
Honeywell
International—Frankford
Plant).
Vicinity Energy Philadelphia—Schuylkill
Station (formerly referenced as Veolia
Energy Philadelphia—Schuylkill Station).
Kinder Morgan Liquid Terminals, LLC—
Philadelphia Terminal (formerly referenced as Kinder Morgan Liquid Terminals, LLC).
Naval Surface Warfare Center—Philadelphia Division (formerly referenced as
Naval
Surface
Warfare
Center—
Carderock Division, Ship Systems Engineering Station (NSWCCD–SSES)).
Newman and Company, Inc (formerly referenced as Paperworks Industries, Inc).
Philadelphia Energy Solutions Refining
and Marketing LLC (formerly referenced
as Philadelphia Energy Solutions—Refining and Marketing, LLC).
Philadelphia Shipyard Inc ..........................
Exelon Generation Company—Richmond
Generating Station.
Grays Ferry Cogeneration Partnership—
Schuylkill Station.
1 The
*
*
Additional explanations/§§ 52.2063 and
52.2064 citations 1
EPA approval date
*
11/1/2021, [insert Federal Register citation].
*
52.2064(f)(1).
3/4/2020
11/1/2021, [insert Federal Register citation].
52.2064(f)(4).
Philadelphia ....
4/20/2020
11/1/2021, [insert Federal Register citation].
52.2064(f)(5).
IP16–000235 ...
Philadelphia ....
3/20/2020
11/1/2021, [insert Federal Register citation].
52.2064(f)(6).
IP16–000223 ...
Philadelphia ....
3/31/2020
52.2064(f)(7).
IP–16–00269 ...
Philadelphia ....
4/24/2020
11/1/2021, [insert Federal Register citation].
11/1/2021, [insert Federal Register citation].
IP16–000300 ...
Philadelphia ....
4/8/2020
52.2064(f)(9).
IP16–000246 ...
Philadelphia ....
4/20/2020
IP–16–000250
Philadelphia ....
3/4/2020
11/1/2021, [insert Federal Register citation].
11/1/2021, [insert Federal Register citation].
11/1/2021, [insert Federal Register citation].
IP16–000276 ...
Philadelphia ....
3/5/2020
IP16–000249 ...
Philadelphia ....
IP16–000233 ...
*
52.2064(f)(8).
52.2064(f)(2).
52.2064(f)(3).
cross-references that are not § 52.2064 are to material that pre-date the notebook format. For more information, see § 52.2063.
*
*
*
*
*
3. Amend § 52.2064 by adding
paragraph (f) 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).
*
lotter on DSK11XQN23PROD with RULES1
State
effective
date
County
*
*
*
*
(f) Approval of source-specific RACT
requirements for the 2008 8-hour ozone
national ambient air quality standard for
the facilities listed in this paragraph are
incorporated as specified. (Rulemaking
Docket No. EPA–OAR–2020–0598).
(1) AdvanSix Resins & Chemicals
LLC—Frankford Plant—Incorporating
by reference RACT Plan Approval No.
IP16–000276, revised and effective
March 5, 2020, which supersedes the
prior RACT Plan Approval effective
February 9, 2016. See also the Federal
Register of October 7, 2016, for prior
RACT approval.
(2) Exelon Generation Company—
Richmond Generating Station—
Incorporating by reference RACT Plan
Approval No. IP16–000246, effective
April 20, 2020 which supersedes the
prior RACT Plan Approval, effective
February 9, 2016. See also the Federal
Register of October 7, 2016, for prior
RACT approval.
(3) Grays Ferry Cogeneration
Partnership—Incorporating by reference
RACT Plan Approval No. IP–16–000250,
effective March 4, 2020, which
supersedes RACT Plan Approval,
effective January 9, 2015. See also the
VerDate Sep<11>2014
16:50 Oct 29, 2021
Jkt 256001
Federal Register of October 7, 2016, for
prior RACT approval.
(4) Vicinity Energy Philadelphia—
Schuylkill Station—Incorporating by
reference RACT Plan Approval No.
IP16–000249, effective March 4, 2020,
which supersedes RACT Plan Approval,
effective February 9, 2016. See also the
Federal Register of October 7, 2016, for
prior RACT approval.
(5) Kinder Morgan Liquids Terminals,
LLC—Philadelphia Terminal—
Incorporating by reference RACT Plan
Approval No. IP16–000233, effective
April 20, 2020, which supersedes RACT
Plan Approval, effective February 9,
2016. See also the Federal Register of
October 7, 2016, for prior RACT
approval.
(6) Naval Surface Warfare Center—
Philadelphia Division—Incorporating by
reference RACT Plan Approval No.
IP16–000235, effective March 20, 2020,
which supersedes the prior RACT Plan
Approval, effective February 9, 2016.
See also the Federal Register of October
7, 2016, for prior RACT approval.
(7) Newman and Company, Inc.—
Incorporating by reference RACT Plan
Approval No. IP16–000223, effective
March 31, 2020, which supersedes
RACT Plan Approval, effective January
9, 2015. See also the Federal Register of
October 7, 2016, for prior RACT
approval.
(8) Philadelphia Energy Solutions
Refining and Marketing LLC.—
Incorporating by reference RACT Plan
PO 00000
Frm 00020
Fmt 4700
Sfmt 4700
Approval No. IP–16–00269, effective
April 24, 2020, which supersedes the
RACT Plan Approval effective February
9, 2016. See also the Federal Register of
October 7, 2016, for prior RACT
approval.
(9) Philadelphia Shipyard Inc.—
Incorporating by reference RACT Plan
Approval No. IP16–000300, effective
April 8, 2020.
[FR Doc. 2021–22571 Filed 10–29–21; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2020–0601; FRL–9111–01–
OCSPP]
Fluensulfone; Pesticide Tolerances
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This regulation establishes
and removes tolerances for residues of
fluensulfone in or on multiple crops
that are identified later in this
document. The Interregional Research
Project Number 4 (IR–4) requested these
tolerance actions under the Federal
Food, Drug, and Cosmetic Act (FFDCA).
DATES: This regulation is effective
November 1, 2021. Objections and
requests for hearings must be received
SUMMARY:
E:\FR\FM\01NOR1.SGM
01NOR1
Agencies
[Federal Register Volume 86, Number 208 (Monday, November 1, 2021)]
[Rules and Regulations]
[Pages 60170-60178]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2021-22571]
[[Page 60170]]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R03-OAR-2020-0598; FRL-9062-02-R3]
Air Plan Approval; Pennsylvania; Reasonably Available Control
Technology (RACT) Determinations for Case-by-Case Sources Under the
2008 8-Hour Ozone National Ambient Air Quality Standards
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
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 individual major sources of volatile organic compounds (VOC) and
nitrogen oxides (NOX) pursuant to the Commonwealth of
Pennsylvania's conditionally approved RACT regulations. In this rule
action, EPA is approving source-specific RACT determinations (``case-
by-case'' or alternative NOX emissions limits) for sources
at nine major NOX and VOC emitting facilities located in
Philadelphia County. These RACT evaluations were submitted to meet RACT
requirements for the 2008 8-hour ozone national ambient air quality
standard (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 December 1, 2021.
ADDRESSES: EPA has established a docket for this action under Docket ID
Number EPA-R03-OAR-2020-0598. 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: Mr. Riley Burger, Permits Branch
(3AD10), Air and Radiation Division, U.S. Environmental Protection
Agency, Region III, 1650 Arch Street, Philadelphia, Pennsylvania 19103.
The telephone number is (215) 814-2217. Mr. Burger can also be reached
via electronic mail at [email protected].
SUPPLEMENTARY INFORMATION:
I. Background
On February 9, 2021, EPA published a notice of proposed rulemaking
(NPRM). 86 FR 8743. In the NPRM, EPA proposed approval of case-by-case
RACT determinations or alternative NOX emissions limits for
sources at nine facilities in Philadelphia County, as EPA found that
the RACT controls for these sources met the CAA RACT requirements for
the 2008 8-hour ozone NAAQS. PADEP, on behalf of Philadelphia Air
Management Services (AMS), submitted the SIP revisions for sources at
these facilities on May 7, 2020.
Under certain circumstances, states are required to submit SIP
revisions to address RACT requirements for both 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 are therefore
subject to RACT, 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
in any ozone nonattainment areas outside of moderate or above are
subject to source thresholds 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 non-CTG
VOC RACT, 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
non-CTG major VOC sources and major NOX sources. The
requirements of the RACT I rule remain as previously approved in
Pennsylvania's SIP and continue to be implemented as RACT.\1\ On
September 26, 2017, PADEP submitted a letter, 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.
---------------------------------------------------------------------------
\1\ The RACT I Rule was approved by EPA into the Pennsylvania
SIP on March 23, 1998. 63 FR 13789. Through this rule, certain
source-specific RACT I requirements will be superseded by more
stringent requirements. See Section II of this preamble.
---------------------------------------------------------------------------
On May 9, 2019, EPA conditionally approved the RACT II rule based
on the commitments PADEP made in its September 22, 2017 letter.\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 plan 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 (i.e., by 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 NOX averaging plan limits. This rule is
based on EPA's review of one of these SIP submissions.
---------------------------------------------------------------------------
\2\ On August 27, 2020, the Third Circuit Court of Appeals
vacated three provisions of Pennsylvania's presumptive RACT II rule
applicable to certain coal-fired power plants. Sierra Club v. EPA,
No. 19-2562 (3rd Cir. August 27, 2020). None of the sources in this
rule are subject to the presumptive RACT II provisions at issue in
the Sierra Club decision.
---------------------------------------------------------------------------
The SIP revisions in this action only establish 2008 8-hour ozone
NAAQS RACT requirements. Applicable RACT requirements under the CAA for
sources located in Philadelphia for the 1997 8-hour ozone NAAQS were
previously satisfied. See 81 FR 69687 (October 7, 2016).
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
NOX averaging plan limits and/or case-by-case RACT
requirements for major sources in Pennsylvania
[[Page 60171]]
subject to 25 Pa. Code 129.98 or 129.99. Among the Pennsylvania SIP
revisions submitted by PADEP were case-by-case RACT determinations and
alternative NOX emissions limits for certain sources in
Philadelphia County, which PADEP submitted on behalf of AMS. PADEP's
submission included SIP revisions pertaining to source-specific RACT
requirements for the existing emissions units at each of the major
sources of NOX and/or VOC that required a source-specific
RACT determination or alternative NOX emissions limits for
major sources seeking such limits.
In the case-by-case RACT determinations submitted by PADEP on
behalf of AMS, an evaluation was completed to determine if previously
SIP-approved, case-by-case RACT emissions limits or operational
controls were more stringent than the new RACT II presumptive or case-
by-case requirements. If more stringent, the previously approved RACT
requirements will continue to apply to the applicable source and are
included in the new RACT II permit. If the new case-by-case RACT II
requirements are more stringent than the previously approved RACT
requirements, then the RACT II requirements will supersede the prior
RACT requirements.\3\
---------------------------------------------------------------------------
\3\ While the prior SIP-approved RACT permit will remain part of
the SIP, this RACT II rule will incorporate by reference the RACT II
requirements through the RACT II permit, which will also contain any
more stringent requirements from the previously approved RACT
permit.
---------------------------------------------------------------------------
In AMS' 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 approving SIP revisions pertaining to case-by-case
RACT requirements and alternative NOX emissions limits for
sources at nine major NOX and/or VOC emitting facilities in
Philadelphia County, as summarized in Table 1 in this document.
Table 1--Nine Major NOX and/or VOC Emitting Facilities in Pennsylvania Subject to Source-Specific RACT II
Determinations Under the 2008 8-Hour Ozone NAAQS
----------------------------------------------------------------------------------------------------------------
1997 8-hour ozone
Major source (county) RACT source? Major source pollutant RACT II permit (effective date)
(RACT I) (NOX and/or VOC)
----------------------------------------------------------------------------------------------------------------
AdvanSix Resins & Chemicals Yes.............. NOX and VOC.............. IP16-000276 (3/5/2020).
LLC--Frankford Plant
(formerly Honeywell
International--Frankford
Plant).
Exelon Generation Company-- Yes.............. NOX...................... IP16-000246 (4/20/2020).
Richmond Generating Station.
Grays Ferry Cogeneration Yes.............. NOX...................... IP-16-000250 (3/4/2020).
Partnership--Schuylkill
Station.
Vicinity Energy Philadelphia-- Yes.............. NOX...................... IP16-000249 (3/4/2020).
Schuylkill Station (formerly
Veolia Energy Philadelphia--
Schuylkill Station).
Kinder Morgan Liquids Yes.............. VOC...................... IP16-000233 (4/20/2020).
Terminals, LLC--Philadelphia
Terminal.
Naval Surface Warfare Center-- Yes.............. NOX...................... IP16-000235 (3/20/2020).
Philadelphia Division
formerly Naval Surface
Warfare Center--Carderock
Division, Ship Systems
Engineering Station).
Newman and Company, Inc Yes.............. NOX...................... IP-000223 (3/31/2020).
(formerly Paperworks
Industries, Inc).
Philadelphia Energy Solutions Yes.............. NOX and VOC.............. IP-16-00269 (4/24/2020).
Refining and Marketing LLC.
Philadelphia Shipyard Inc..... No............... VOC...................... IP16-000300 (4/8/2020).
----------------------------------------------------------------------------------------------------------------
The case-by-case RACT determinations submitted by PADEP, on behalf
of AMS, consist of an evaluation of all reasonably available controls
at the time of evaluation for each affected emissions unit, resulting
in an AMS determination of what specific emissions limit or control
measures satisfy RACT for that particular unit. The adoption of new,
additional, or revised emissions 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 AMS to the source. Similarly, AMS' 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 into 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 of this
preamble, 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-2019-0657.\4\ EPA is
incorporating by reference in the Pennsylvania SIP, via the RACT II
permits, source-specific RACT emissions limits and control measures and
alternative NOX emissions limits under the 2008 8-hour ozone
NAAQS for certain major sources of NOX and VOC emissions.
---------------------------------------------------------------------------
\4\ The RACT II permits included in the docket for this rule 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 AMS' determinations of source-
specific RACT II controls for individual emission units at major
sources of NOX and/or VOC in Philadelphia, where those units
are not covered by or cannot meet Pennsylvania's presumptive RACT
regulation or where included in a NOX averaging plan. After
thorough review and evaluation of the information provided by AMS in
the SIP revision submittals for sources at nine major NOX
and/or VOC emitting facilities in Philadelphia, EPA found that: (1)
AMS' 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) AMS' determinations on alternative NOX
emissions 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) AMS'
determinations are consistent with the CAA, EPA regulations, and
applicable EPA guidance.
[[Page 60172]]
AMS, in its RACT II determinations, considered the prior source-
specific RACT requirements and, where more stringent, retained those
prior RACT 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 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 the NAAQS, reasonable further
progress, or other applicable requirements under section 110(l) of the
CAA.
Other specific requirements of the 2008 8-hour ozone NAAQS case-by-
case RACT determinations and alternative NOX emissions
limits and the rationale for EPA's proposed action are explained more
thoroughly in the NPRM, and its associated technical support document
(TSD), and will not be restated here.
III. EPA's Response to Comments Received
EPA received comments from three commenters on the February 9, 2021
NPRM. 86 FR 8743. 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 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 NAAQS 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 and allow for comment on any such modeling information or other
information utilized in the demonstration that the NAAQS will be
protected.\5\
---------------------------------------------------------------------------
\5\ This summary of the comment includes supplemental
information provided by the commenter in a similar comment to EPA's
proposed rulemaking in EPA-R03-OAR-2020-0597.
---------------------------------------------------------------------------
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 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. For
subject sources located in Philadelphia, the City of Philadelphia's AMS
is the government agency responsible for making such determinations.
---------------------------------------------------------------------------
\6\ 40 CFR 52.2020(d)(1).
\7\ 84 FR 20274 (May 9, 2019).
---------------------------------------------------------------------------
As required by Pennsylvania's RACT II regulations, AMS then
conducted, for sources seeking a CbC determination, an analysis
examining what air pollution controls were available for those
individual sources to determine the lowest emissions 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\ For sources seeking an alternative
NOX emissions limit, AMS reviewed the NOX
averaging plan to determine that the alternative NOX
emissions limits demonstrated that the emissions under the averaging
plan were equivalent to emissions as if the individual sources were
operating in accordance with the applicable presumptive limit.
---------------------------------------------------------------------------
\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 source-specific RACT II determinations, AMS has
established NOX and VOC limits and requirements for various
sources that either reaffirm existing emissions limits or makes the
limits more stringent. PADEP, on behalf of AMS, 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 nine facilities in Philadelphia
County. 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.
For these reasons, EPA 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 RACT II 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
[[Page 60173]]
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); 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. In both cases, the
state 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. In both Kentucky Resources and Indiana, the court 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. 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 Guardians 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 Guardians 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 Guardians 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, AMS is not relaxing standards or eliminating a
program; rather, AMS is only re-evaluating the technical and economic
feasibility of air pollution controls for subject air pollution sources
as required by implementation of the 2008 8-hour NAAQS. Based on that
review, AMS, as explained in more detail below, has made determinations
that either retain or make more stringent existing NOX
emissions limits. Emissions are not expected to increase, and will
likely decrease, as a result of AMS' RACT II NOX CbC
determinations and EPA's approval hereof. Under these circumstances,
AMS' demonstration to meet the requirements of section 110(l) for its
source-specific 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 source-
specific NOX RACT determinations are preserving the status
quo air quality or achieving additional reductions beyond the status
quo.
---------------------------------------------------------------------------
\9\ 759 F.3d at 1074.
---------------------------------------------------------------------------
With this rule action, EPA is only approving revisions that add
specific NOX and VOC source-specific RACT II determinations
to the Pennsylvania SIP. In the subject RACT II source-specific
determinations, AMS has made an adequate showing that its source-
specific determinations for individual sources at the nine 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 memoranda and related
documents, which are included in the docket for this rule, AMS
evaluated both the technical and economic feasibility of various
control equipment for these sources and used that evaluation to
determine the RACT II requirements. AMS 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 40 CFR part 51, appendix V. The record supporting EPA's
approval of AMS' source-specific 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 in this rule identified as objectionable in the
comment break down into the categories listed below. As explained in
the proposed rulemaking document, 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--Kinder Morgan Liquid Terminals,
LLC is a major source VOC emitting facility that is a minor source of
NOX. As such, individual VOC sources at this facility must
comply with RACT II requirements. EPA's approval in this rule for this
facility only relates to specific CbC VOC RACT II determinations. EPA's
approval of the Pennsylvania CbC RACT II SIP revision for sources at
for this facility does not involve NOX emissions, maintains
the status quo in VOC emissions, and does not result in an increase in
VOC or NOX emissions. Therefore, as explained previously,
EPA has determined this SIP revision will not interfere with any
applicable requirement concerning attainment, reasonable further
progress, or any other applicable requirement of the CAA pursuant to
section 110(l).
Facilities with CbC NOX Sources--The following
facilities 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:
Exelon Generation Company--Richmond Generating Station--EPA
proposed to approve AMS' RACT II CbC NOX determination for
two combustion turbines at this facility. After determining that there
were no new technically and economically feasible NOX
controls for these sources, AMS has determined that the RACT II
NOX is continuing to comply with the existing NOX
emissions limits and capacity factor.\10\ Through retention of the
existing emissions limits and restrictions, AMS has demonstrated that
the status quo in NOX emissions has been maintained. As
such, EPA's approval of the Pennsylvania SIP revision for the
individual sources at this facility is adequately justified under
section 110(l).
---------------------------------------------------------------------------
\10\ See AMS' InterOffice Memo, dated April 20, 2020, which is
part of the docket for this rule.
---------------------------------------------------------------------------
Grays Ferry Cogeneration Partnership--Schuylkill Station (GFCP) and
Vicinity Energy Philadelphia--Schuylkill Station (Vicinity)--The two
facilities hold separate operating permits, but they share a geographic
[[Page 60174]]
location and are considered a single source for title V and New Source
Review purposes. EPA proposed to approve AMS' RACT II determination
related to a facility-wide NOX averaging plan for three
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 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. GFCP and
Vicinity will be averaging the NOX emissions for three
sources to meet the RACT II requirements, an alternative emissions
limit, that will be at least as stringent as the presumptive emissions
limits, which were conditionally approved by EPA in a prior rule.
Additionally, AMS has retained all of the individual emissions limits
from the prior RACT approval.\11\ AMS' approval of the alternative
NOX emissions limit 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 emissions limit. The alternative NOX
emissions limit does not eliminate the prior individual emissions
limits. Through these measures, AMS has demonstrated that the status
quo for NOX emissions has been maintained. As such, EPA's
approval of the Pennsylvania SIP revision for the individual sources at
these facilities is adequately justified under section 110(l).
---------------------------------------------------------------------------
\11\ See 84 FR 20274 (May 9, 2019) as to EPA's conditional
approval of the presumptive limit and AMS' Inter Office Memo, dated
March 4, 2020, which is part of the docket for this rule.
---------------------------------------------------------------------------
Philadelphia Energy Solutions Refining and Marketing LLC (PES)--EPA
proposed to approve AMS' RACT II CbC NOX determinations for
numerous sources at this facility and its alternative NOX
emissions limits for a number of heaters and boilers. At the time AMS
issued the current RACT Plan Approval to PES in April 2020, which
incorporated its RACT II NOX determinations, refining
operations at the PES facility had been shut down. The refinery has
been closed since June 2019, and the facility has been sold to a new
owner. AMS' proposed RACT II SIP revision does not authorize new
operations at the facility, but rather incorporates RACT requirements
for major NOX and VOC sources in operation as of 2012 into
the SIP.
For the CbC NOX sources at the facility, AMS has
determined that all proposed 2008 NOX RACT requirements
(such as emissions limits, control technologies like selective
catalytic reduction (SCR) and low NOX burners, continuous
emissions monitoring systems (CEMs), combustion tuning, and good
combustion practices), are at least as stringent as the prior 1997 8-
hour NOX RACT requirements and has included them in the new
2020 RACT permit, which will be incorporated into the Pennsylvania SIP
through this action. At the same time, AMS also approved for a group of
heaters and boilers alternative NOX emissions limits through
the use of three NOX averaging plans 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 NOX emissions limit as long as it demonstrates that the
resulting NOX emissions using a 30-day rolling average would
not be greater than the NOX emissions from the group of
included sources if they each complied with the applicable presumptive
NOX RACT emissions limit as individual sources. The facility
is required to average the NOX emissions for three groups of
sources to meet the RACT II requirements, an alternative emissions
limit, that will be at least as stringent as the presumptive emissions
limit, which was conditionally approved by EPA in a prior rule.\12\
---------------------------------------------------------------------------
\12\ See 84 FR 20274 (May 9, 2019) as to EPA's conditional
approval of the presumptive limit and AMS' Inter Office Memo, dated
April 24, 2020, which is part of the docket for this rule.
---------------------------------------------------------------------------
Through retention of the existing emissions limits and the approval
of the alternative NOX emissions limits at the facility, AMS
has demonstrated that the status quo in NOX emissions has
been maintained. As such, EPA's approval of the Pennsylvania SIP
revision for the individual sources at this facility is adequately
justified under section 110(l).
As described above, EPA determined that AMS adequately justified
its RACT II CbC NOX determinations and alternative
NOX emissions limits. 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.\13\ 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.
---------------------------------------------------------------------------
\13\ 77 FR 9532 (February 17, 2012).
---------------------------------------------------------------------------
This modeling data analysis from Colorado does not trigger a need
for EPA, Pennsylvania, or AMS to conduct modeling on the impact of
NOX emissions from each individual source at issue in this
rule 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 Philadelphia RACT II sources are too significant to
rely on the Bighorn facility modeling results to serve as surrogate
modeling indicating that the Philadelphia 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 Philadelphia.
Further, the commenter has not presented any specific information
suggesting the RACT II CbC NOX determinations or alternative
NOX emissions limits 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 AMS' RACT II CbC NOX
determinations or alternative NOX emissions limits for
sources at the five subject facilities.
Comment 2: The commenter states that minor errors are present in
the technical and economic feasibility analysis of available controls
throughout the proposed rulemaking. The commenter asserts that in
several instances, the discussion of costs incorrectly led to the
conclusion that certain controls were technically infeasible, rather
than identifying those controls as technically feasible and then
evaluating the cost issues in the economic analysis. The specific
[[Page 60175]]
instances in which commenter claims there are minor errors are in the
evaluation of a fuel switch to natural gas, water/steam injection, and
SCR for boilers.
The commenter also raises concern with the use, in the economic
feasibility analysis, of outdated interest rates that are not
reflective of current economic conditions and the consumer price index
(CPI) to adjust air pollution control costs to current dollar values.
Ultimately, the commenter acknowledges that if the RACT evaluations
were redone in a manner to address the identified concerns, the control
technologies determined to be RACT would not change.
Response 2: The commenter correctly asserts that an evaluation of
the technical feasibility of available controls should be conducted
before evaluating the economic feasibility of the remaining available
controls. 25 Pa. Code 129.92(b) and 129.99(d)(1). The TSD, which is
included in the docket file for this action, explains the basis for
EPA's approval of the RACT determinations included in this rule. From
its review of the specific RACT determinations made by AMS in this
rule, EPA cannot locate a source where there was a determination where
water/steam injection was identified as technically infeasible.
Similarly, except for two heaters at the PES facility, there are no
determinations where SCR on a boiler was identified as technically
infeasible. For the two exceptions, Heaters 860-2H8 and 864-PH7, SCR
was determined to be infeasible because of physical space constraints,
not due to the use of ammonia or urea as identified by the commenter.
As to the commenter's remarks about fuel switching, it appears that
they may apply to the Exelon Generating Company--Richmond Station where
a fuel switch to natural gas was determined to be technically
infeasible for Combustion Turbine #91 and #92. In this instance, Exelon
identified the large-scale costs and related regulatory requirements as
technical impediments to installing a natural gas line to the facility,
and AMS agreed with this analysis and determined that it was not
technically feasible. Whether or not AMS' conclusion on the technical
feasibility analysis was sufficient does not change the final
conclusion on the overall feasibility of the potential use of fuel
switching for the sources at this facility. EPA agrees with the
commenter that determining fuel switching as a technically feasible
control would not change the determination that this control is
ultimately infeasible as RACT for the sources at hand and is finalizing
AMS' proposed RACT requirements.
EPA also agrees with the commenter that choosing suitable interest
rates and cost escalation factors is a requirement of RACT
determinations. Per 25 Pa. Code 129.92(b)(4), the cost effectiveness
evaluation must be consistent with the OAQPS Control Cost Manual
(Fourth Edition) EPA 450/3-90-006 January 1990 (Control Cost Manual)
and subsequent revisions.\14\ The Control Cost Manual addresses
appropriate use of the CPI and lays out general principals to make
accurate escalation calculations and choose appropriate interests
rates. However, the Control Cost Manual in its current form does not
specifically prohibit use of the CPI.
---------------------------------------------------------------------------
\14\ The OAQPS Control Cost Manual referenced in 25 Pa. Code
129.92(b)(4) is also known as the EPA Air Pollution Control Cost
Manual. OAQPS is the acronym for EPA's Office of Air Quality
Planning and Standards.
---------------------------------------------------------------------------
The commenter did not specify which economic feasibility
determinations in this rule contain questionable interest rates or cost
escalations but recognizes that updates to such factors in the economic
analysis would not necessarily change the final RACT determinations.
These factors are among many other values used in a complex, multi-
factor cost analysis. EPA agrees it is not clear that revised interest
rate or cost escalations in the economic analysis would change the
final conclusions of the determinations contained in this rule. Without
a more specific allegation from the commenter about the sources in
question, the commenter's allegations are too general and speculative
in nature to prevent EPA from approving AMS' RACT II CbC determinations
for sources at the nine subject facilities.
Comment 3: The commenter raises concern with the Grays Ferry
Cogeneration Partnership and Vicinity Energy NOX averaging
plan and the Philadelphia Energy Solutions Refining and Marketing LLC
(PES) NOX averaging plan. Specifically the commenter
asserts: (1) In order to be protective of the 8-hour average of the
2008 ozone NAAQS, particularly during ozone season, these RACT
determinations should include short term emissions limits on a calendar
day basis (as is done in New Jersey and other states), rather than a 30
operating day rolling average; (2) Grays Ferry Cogeneration Partnership
and Vicinity Energy should be required to evaluate control options of
combusting only natural gas, replacing No. 6 oil with No. 2 oil, and
additional NOX controls; and (3) due to the recent events at
PES, including shutting down operations, bankruptcy, and sale, EPA
should not approve the proposed SIP revision until a new owner begins
operations at the facility.
More generally, the commenter asserts that EPA should establish
term limits for RACT plan approvals and ensure that facilities re-
evaluate RACT plans to incorporate any future advancements in
technology as is required by New Jersey RACT rules.
Response 3: In its conditional approval of Pennsylvania's overall
RACT II program at 25 Pa. Code 129.96-129.100 (84 FR 20274, May 9,
2019), EPA explained that under 25 Pa. Code 129.98, affected major
sources unable to meet the applicable presumptive RACT emissions
limitation may choose to comply with alternative NOX
requirements based on averaging NOX emissions from multiple
sources. Specifically, EPA explained that averaging plans pursuant to
Pennsylvania's RACT II regulations are intended to demonstrate 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. Thus, the use of a 30-day rolling
average for NOX averaging plans under Pennsylvania's RACT II
program was previously approved by EPA.
EPA guidance does highlight the need for emission controls that are
reasonably consistent with protecting a short-term NAAQS such as ozone.
However, in those cases where an emissions limit for a RACT control can
be quantified, EPA guidance states that averaging periods for such
limits should be as short as practicable and in no case longer than 30
days. See the January 20, 1984 EPA guidance memorandum titled
``Averaging Times for Compliance with VOC Emissions Limits--SIP
Revision Policy.''
In the instance of Grays Ferry Cogeneration Partnership and
Vicinity Energy, the facilities are using an averaging plan to limit
NOX emissions from the combustion turbine, Boiler #25, and
Boiler #26 to no greater than the NOX emissions that would
have resulted had each individual source complied with the presumptive
RACT limits of 25 Pa. Code 129.97(g)(2)(i)(A) and (B) and
129.97(g)(1)(i) and (ii). PES is using averaging plans to limit
emissions from Heaters 137 F-1, 137 F-2, 137 F-3, 1332 H-400, and 1332
H-401 and #3 Boilerhouse Boilers #37, #39, and #40 to no greater than
the NOX emissions that would have resulted had each
individual source complied with the presumptive RACT limits of 25 Pa.
Code 129.97(g)(1)(iv). In each instance,
[[Page 60176]]
the 30-day rolling average used for demonstrating compliance is
consistent with the requirements contained in Pennsylvania's previously
approved RACT II program.
EPA disagrees with the commenter that Grays Ferry Cogeneration
Partnership and Vicinity Energy should evaluate the technical and
economic feasibility of certain alternative control options. The
evaluation of alternative controls is only a requirement for sources
opting for case-by-case RACT evaluation under 25 Pa. Code 129.99.
Sources at the subject facilities are complying with RACT through the
NOX emission averaging plan provisions under 25 Pa. Code
129.98. Accordingly, they are not required to evaluate potential
alternative control options as required by the case-by-case option.
EPA also disagrees with the commenter's recommendation to
disapprove the NOX averaging plan for the PES facility and
wait for action by a new owner. EPA acknowledges the commenter's
references to the shutdown of refining operations at the PES facility
in June 2019, the subsequent bankruptcy filing by PES, and the
prospective sale of the facility. Nevertheless, Pennsylvania's RACT II
requirements apply to major NOX and VOC emitting facilities
that were in existence on or before July 20, 2012. 25 Pa. Code 129.96.
Proposed NOX averaging plans were required to be submitted
to the government by October 24, 2016. 25 Pa. Code 129.98. As AMS'
approval of the NOX averaging plans for certain sources at
PES was submitted to EPA as a SIP revision, meets the requirements of
Pennsylvania's RACT II NOX averaging provisions, and has not
been withdrawn, EPA is finalizing the proposed RACT II requirements for
those sources.
Finally, EPA declines to establish term limits for RACT plan
approvals to ensure the periodic re-evaluation of technologies as
required by New Jersey's RACT rules. The Clean Air Act and the
requirements to implement RACT are designed to protect public health
and the environment. However, the only factors EPA is legally required
to consider for approving RACT are those in the statute, EPA's
regulations, and the SIP-approved Pennsylvania implementing
regulations. Term limits for RACT plan approvals for periodic re-
evaluation of technologies is not a statutory or regulatory requirement
for approval of these RACT determinations. Even without such term
limits, RACT is periodically reevaluated in non-attainment areas after
the promulgation of a new ozone NAAQS.
IV. Final Action
EPA is approving the case-by-case RACT determinations and/or
alternative NOX emissions limits for sources at nine major
NOX and VOC emitting facilities in Philadelphia, as required
to meet obligations pursuant to the 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 NOX averaging plan limits
under the 2008 8-hour ozone NAAQS for certain major sources of VOC and
NOX in Philadelphia County. 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.\15\
---------------------------------------------------------------------------
\15\ 62 FR 27968 (May 22, 1997).
---------------------------------------------------------------------------
V. 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
[[Page 60177]]
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 January 3, 2022. 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 nine facilities for 2008 8-hour ozone NAAQS may
not be challenged later in 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: October 8, 2021.
Diana Esher,
Regional Administrator, Region III.
For the reasons set out in the preamble, 40 CFR part 52 is amended
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 ``Exelon Generation Company--Richmond
Generating Station''; ``Grays Ferry Cogeneration Partnership--
Schuylkill Station''; ``Honeywell International--Frankford Plant'';
``Kinder Morgan Liquid Terminals, LLC''; ``Naval Surface Warfare
Center--Carderock Division, Ship Systems Engineering Station (NSWCCD-
SSES)''; ``Paperworks Industries, Inc''; ``Philadelphia Energy
Solutions--Refining and Marketing, LLC''; and ``Veolia Energy
Philadelphia--Schuylkill Station'';
0
b. Adding entries at the end of the table for ``AdvanSix Resins &
Chemicals LLC--Frankford Plant (formerly referenced as Honeywell
International--Frankford Plant)''; ``Vicinity Energy Philadelphia--
Schuylkill Station (formerly referenced as Veolia Energy Philadelphia--
Schuylkill Station)''; ``Kinder Morgan Liquid Terminals, LLC--
Philadelphia Terminal (formerly referenced as Kinder Morgan Liquid
Terminals, LLC)''; ``Naval Surface Warfare Center--Philadelphia
Division (formerly referenced as Naval Surface Warfare Center--
Carderock Division, Ship Systems Engineering Station) (NSWCCD-SSES))'';
``Newman and Company, Inc (formerly referenced as Paperworks
Industries, Inc)''; ``Philadelphia Energy Solutions Refining and
Marketing LLC (formerly referenced as Philadelphia Energy Solutions--
Refining and Marketing, LLC)''; and ``Philadelphia Shipyard Inc.''; and
0
c. Adding additional entries at the end of the table for ``Exelon
Generation Company--Richmond Generating Station'' and ``Grays Ferry
Cogeneration Partnership--Schuylkill Station''.
The revisions and additions read as follows:
Sec. 52.2020 Identification of plan.
* * * * *
(d) * * *
(1) * * *
----------------------------------------------------------------------------------------------------------------
Additional
explanations/
State EPA approval Sec. Sec.
Name of source Permit No. County effective date 52.2063 and
date 52.2064
citations \1\
----------------------------------------------------------------------------------------------------------------
* * * * * * *
Exelon Generation Company-- PA-51-4903...... Philadelphia.... 02/09/16 10/07/16, 81 FR Supersedes
Richmond Generating Station. 69691. previously
approved RACT
permit. See
also
52.2064(f)(2).
Grays Ferry Cogeneration PA-51-4944...... Philadelphia.... 1/09/15 10/7/16, 81 FR Source is
Partnership--Schuylkill 69691. aggregated
Station. with Veolia
Energy
Efficiency,
LLC and Veolia
Energy--Schuyl
kill Station.
See also
52.2064(f)(3).
Honeywell International-- PA-51-1151...... Philadelphia.... 02/09/16 10/07/16, 81 FR Supersedes
Frankford Plant. 69691. previously
approved RACT
permit. Source
was formerly
Sunoco
Chemicals,
Frankford
Plant. See
also
52.2064(f)(1).
Kinder Morgan Liquid PA-51-5003...... Philadelphia.... 02/09/16 10/7/16, 81 FR Supersedes
Terminals, LLC. 69691. previously
approved RACT
permit. Source
was formerly
GATX Terminal
Corporation.
See also
52.2064(f)(5).
Naval Surface Warfare Center-- PA-51-9724...... Philadelphia.... 02/09/16 10/7/16, 81 FR Supersedes
Carderock Division, Ship 69691. previously
Systems Engineering Station approved RACT
(NSWCCD-SSES). permits.
Source was
formerly U.S.
Navy, Naval
Surface
Warfare
Center,
Carderock
Division
(NSWCCD). See
also
52.2064(f)(6).
Paperworks Industries, Inc... PA-51-1566...... Philadelphia.... 1/09/15 10/7/16, 81 FR Supersedes
69691. previously
approved RACT
permit. Source
was formerly
Jefferson
Smurfit, Corp./
Container
Corp. of
America. See
also
52.2064(f)(7).
Philadelphia Energy PA-51-01501; PA- Philadelphia.... 02/09/16 10/7/2016, 81 Supersedes
Solutions--Refining and 51-01517. FR 69691. previously
Marketing, LLC. approved RACT
permit. Source
was formerly
Sunoco Inc.
(R&M)--Philade
lphia. See
also
52.2064(f)(8).
* * * * * * *
Veolia Energy Philadelphia-- PA-51-4942...... Philadelphia.... 02/09/16 10/7/16, 81 FR Supersedes
Schuylkill Station. 69691. previously
approved RACT
permit. Source
was formerly
TRIGEN--Schuyl
kill Station.
Source is
aggregated
with Grays
Ferry
Cogeneration
Partnership
and Veolia
Energy
Efficiency,
LLC. See also
52.2064(f)(4).
[[Page 60178]]
* * * * * * *
AdvanSix Resins & Chemicals IP16-000276..... Philadelphia.... 3/5/2020 11/1/2021, 52.2064(f)(1).
LLC--Frankford Plant [insert
(formerly referenced as Federal
Honeywell International-- Register
Frankford Plant). citation].
Vicinity Energy Philadelphia-- IP16-000249..... Philadelphia.... 3/4/2020 11/1/2021, 52.2064(f)(4).
Schuylkill Station (formerly [insert
referenced as Veolia Energy Federal
Philadelphia--Schuylkill Register
Station). citation].
Kinder Morgan Liquid IP16-000233..... Philadelphia.... 4/20/2020 11/1/2021, 52.2064(f)(5).
Terminals, LLC--Philadelphia [insert
Terminal (formerly Federal
referenced as Kinder Morgan Register
Liquid Terminals, LLC). citation].
Naval Surface Warfare Center-- IP16-000235..... Philadelphia.... 3/20/2020 11/1/2021, 52.2064(f)(6).
Philadelphia Division [insert
(formerly referenced as Federal
Naval Surface Warfare Register
Center--Carderock Division, citation].
Ship Systems Engineering
Station (NSWCCD-SSES)).
Newman and Company, Inc IP16-000223..... Philadelphia.... 3/31/2020 11/1/2021, 52.2064(f)(7).
(formerly referenced as [insert
Paperworks Industries, Inc). Federal
Register
citation].
Philadelphia Energy Solutions IP-16-00269..... Philadelphia.... 4/24/2020 11/1/2021, 52.2064(f)(8).
Refining and Marketing LLC [insert
(formerly referenced as Federal
Philadelphia Energy Register
Solutions--Refining and citation].
Marketing, LLC).
Philadelphia Shipyard Inc.... IP16-000300..... Philadelphia.... 4/8/2020 11/1/2021, 52.2064(f)(9).
[insert
Federal
Register
citation].
Exelon Generation Company-- IP16-000246..... Philadelphia.... 4/20/2020 11/1/2021, 52.2064(f)(2).
Richmond Generating Station. [insert
Federal
Register
citation].
Grays Ferry Cogeneration IP-16-000250.... Philadelphia.... 3/4/2020 11/1/2021, 52.2064(f)(3).
Partnership--Schuylkill [insert
Station. Federal
Register
citation].
----------------------------------------------------------------------------------------------------------------
\1\ The cross-references that are not Sec. 52.2064 are to material that pre-date the notebook format. For more
information, see Sec. 52.2063.
* * * * *
0
3. Amend Sec. 52.2064 by adding paragraph (f) 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).
* * * * *
(f) Approval of source-specific RACT requirements for the 2008 8-
hour ozone national ambient air quality standard for the facilities
listed in this paragraph are incorporated as specified. (Rulemaking
Docket No. EPA-OAR-2020-0598).
(1) AdvanSix Resins & Chemicals LLC--Frankford Plant--Incorporating
by reference RACT Plan Approval No. IP16-000276, revised and effective
March 5, 2020, which supersedes the prior RACT Plan Approval effective
February 9, 2016. See also the Federal Register of October 7, 2016, for
prior RACT approval.
(2) Exelon Generation Company--Richmond Generating Station--
Incorporating by reference RACT Plan Approval No. IP16-000246,
effective April 20, 2020 which supersedes the prior RACT Plan Approval,
effective February 9, 2016. See also the Federal Register of October 7,
2016, for prior RACT approval.
(3) Grays Ferry Cogeneration Partnership--Incorporating by
reference RACT Plan Approval No. IP-16-000250, effective March 4, 2020,
which supersedes RACT Plan Approval, effective January 9, 2015. See
also the Federal Register of October 7, 2016, for prior RACT approval.
(4) Vicinity Energy Philadelphia--Schuylkill Station--Incorporating
by reference RACT Plan Approval No. IP16-000249, effective March 4,
2020, which supersedes RACT Plan Approval, effective February 9, 2016.
See also the Federal Register of October 7, 2016, for prior RACT
approval.
(5) Kinder Morgan Liquids Terminals, LLC--Philadelphia Terminal--
Incorporating by reference RACT Plan Approval No. IP16-000233,
effective April 20, 2020, which supersedes RACT Plan Approval,
effective February 9, 2016. See also the Federal Register of October 7,
2016, for prior RACT approval.
(6) Naval Surface Warfare Center--Philadelphia Division--
Incorporating by reference RACT Plan Approval No. IP16-000235,
effective March 20, 2020, which supersedes the prior RACT Plan
Approval, effective February 9, 2016. See also the Federal Register of
October 7, 2016, for prior RACT approval.
(7) Newman and Company, Inc.--Incorporating by reference RACT Plan
Approval No. IP16-000223, effective March 31, 2020, which supersedes
RACT Plan Approval, effective January 9, 2015. See also the Federal
Register of October 7, 2016, for prior RACT approval.
(8) Philadelphia Energy Solutions Refining and Marketing LLC.--
Incorporating by reference RACT Plan Approval No. IP-16-00269,
effective April 24, 2020, which supersedes the RACT Plan Approval
effective February 9, 2016. See also the Federal Register of October 7,
2016, for prior RACT approval.
(9) Philadelphia Shipyard Inc.--Incorporating by reference RACT
Plan Approval No. IP16-000300, effective April 8, 2020.
[FR Doc. 2021-22571 Filed 10-29-21; 8:45 am]
BILLING CODE 6560-50-P