Approval and Promulgation of Air Quality Implementation Plans; Pennsylvania; Reasonably Available Control Technology (RACT) Determinations for Case-by-Case Sources Under the 1997 and 2008 8-Hour Ozone National Ambient Air Quality Standards, 66257-66264 [2020-21438]
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Federal Register / Vol. 85, No. 202 / Monday, October 19, 2020 / Rules and Regulations
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3. Amend § 52.2033 by adding
paragraph (f) to read as follows:
§ 52.2033
Control strategy: Sulfur oxides.
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(f) EPA approves the attainment
demonstration State Implementation
Plan for the Indiana, PA Nonattainment
Area submitted by the Pennsylvania
Department of Environmental Protection
on October 11, 2017, updated on
February 5, 2020, and corrected permits
and plan approvals submitted on May
13, 2020.
[FR Doc. 2020–23037 Filed 10–16–20; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R03–OAR–2020–0189; FRL–10014–
98–Region 3]
Approval and Promulgation of Air
Quality Implementation Plans;
Pennsylvania; Reasonably Available
Control Technology (RACT)
Determinations for Case-by-Case
Sources Under the 1997 and 2008 8Hour Ozone National Ambient Air
Quality Standards
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
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 action, EPA is only
approving source-specific (also referred
to as ‘‘case-by-case’’) RACT
determinations for four major sources.
These RACT evaluations were
submitted to meet RACT requirements
for the 1997 and 2008 8-hour ozone
national ambient air quality standards
(NAAQS). EPA is approving these
revisions to the Pennsylvania SIP in
accordance with the requirements of the
Clean Air Act (CAA) and EPA’s
implementing regulations.
DATES: This final rule is effective on
November 18, 2020.
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SUMMARY:
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EPA has established a
docket for this action under Docket ID
Number EPA–R03–OAR–2020–0189. All
documents in the docket are listed on
the https://www.regulations.gov
website. Although listed in the index,
some information is not publicly
available, e.g., confidential business
information (CBI) or other information
whose disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available through https://
www.regulations.gov, or please contact
the person identified in the FOR FURTHER
INFORMATION CONTACT section for
additional availability information.
FOR FURTHER INFORMATION CONTACT: Ms.
Emily Bertram, Permits Branch (3AD10),
Air & Radiation Division, U.S.
Environmental Protection Agency,
Region III, 1650 Arch Street,
Philadelphia, Pennsylvania 19103. The
telephone number is (215) 814–5273.
Ms. Bertram can also be reached via
electronic mail at bertram.emily@
epa.gov.
SUPPLEMENTARY INFORMATION:
ADDRESSES:
■
I. Background
On May 5, 2020, EPA published a
notice of proposed rulemaking (NPRM).
85 FR 26647. In the NPRM, EPA
proposed approval of case-by-case
RACT determinations for four sources in
Pennsylvania for the 1997 and 2008 8hour ozone NAAQS. The case-by-case
RACT determinations for these four
sources were included in SIP revisions
submitted by PADEP on November 21,
2017, April 26, 2018, June 26, 2018, and
October 29, 2018.
Under certain circumstances, states
are required to submit SIP revisions to
address RACT requirements for major
sources of NOX and VOC or any source
category for which EPA has
promulgated control technique
guidelines (CTG) for each ozone
NAAQS. Which NOX and VOC sources
in Pennsylvania are considered ‘‘major,’’
and therefore to be addressed for RACT
revisions, is dependent on the location
of each source within the
Commonwealth. Sources located in
nonattainment areas would be subject to
the ‘‘major source’’ definitions
established under the CAA based on
their classification. In the case of
Pennsylvania, sources located in any
areas outside of moderate or above
nonattainment areas, as part of the
Ozone Transport Region (OTR), are
subject to source thresholds of 50 tons
per year (tpy). CAA section 184(b).
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66257
On May 16, 2016, PADEP submitted
a SIP revision addressing RACT under
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
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
approved into Pennsylvania’s SIP and
continue to be implemented.1 On
September 26, 2017, PADEP submitted
a supplemental SIP revision, dated
September 22, 2017, which committed
to address various deficiencies
identified by EPA in their May 16, 2016
‘‘presumptive’’ RACT II rule SIP
revision.
On May 9, 2019, EPA conditionally
approved the RACT II rule based on the
commitments PADEP made in its
September 22, 2017 supplemental SIP
revision. See 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 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, specifically
May 9, 2020. The SIP revisions
addressed in this rule are part of
PADEP’s efforts to meet the conditions
of its supplemental SIP revision and
EPA’s conditional approval of the RACT
II Rule.
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 case-by-case RACT
requirements for major sources in
Pennsylvania subject to 25 Pa. Code
1 The RACT I Rule was approved by EPA into the
Pennsylvania SIP on March 23, 1998. 63 FR 13789.
Through the current rule, certain source-specific
RACT I requirements will be superseded by more
stringent RACT II requirements. See Section II of
this preamble.
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129.99. In the Pennsylvania RACT SIP
revisions, PADEP included a case-bycase RACT determination for the
existing emissions units at each of these
major sources of NOX and/or VOC that
required a source-specific RACT
determination. In PADEP’s RACT
determinations, an evaluation was
completed to determine if previously
SIP-approved, case-by-case RACT
emission limits or operational controls
(herein referred to as RACT I and
contained in RACT I permits) were more
stringent than the new RACT II
presumptive or case-by-case
requirements. If more stringent, the
RACT I requirements will continue to
apply to the applicable source. If the
new case-by-case RACT II requirements
are more stringent than the RACT I
requirements, then the RACT II
requirements will supersede the prior
RACT I requirements.2
Here, EPA is taking action on SIP
revisions pertaining to case-by-case
RACT requirements for four major
sources of NOX and/or VOC in
Pennsylvania, as summarized in Table
1.
TABLE 1—FOUR MAJOR NOX AND/OR VOC SOURCES IN PENNSYLVANIA SUBJECT TO CASE-BY-CASE RACT II
DETERMINATIONS UNDER THE 1997 AND 2008 8-HOUR OZONE NAAQS
1-Hour ozone
RACT source?
(RACT I)
Major source
(county)
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Transco—Salladasburg Station 520 (Lycoming) ....................................
Novipax (Berks) .......................................................................................
Sunoco Partners Marketing & Terminals (Delaware) .............................
Global Advanced Metals USA, Inc. (Montgomery) .................................
Yes
Yes
Yes
Yes
.................
.................
.................
.................
Major source
pollutant
(NOX and/or
VOC)
RACT II permit
(effective date)
NOX and VOC ...
VOC ...................
NOX and VOC ...
VOC ...................
41–00001
06–05036
23–00119
46–00037
(06/06/17).
(12/19/2017).
(01/20/17).
(03/10/17).
The case-by-case RACT
determinations submitted by PADEP
consist of an evaluation of all
reasonably available controls at the time
of evaluation for each affected emissions
unit, resulting in a PADEP
determination of what specific emission
limit or control measures, if any, satisfy
RACT for that particular unit. The
adoption of new, additional, or revised
emission limits or control measures to
existing SIP-approved RACT I
requirements were specified as
requirements in new or revised
Federally enforceable permits (hereafter
RACT II permits) issued by PADEP to
the source. The RACT II permits, which
revise or adopt additional sourcespecific limits and/or controls, have
been submitted as part of the
Pennsylvania RACT SIP revisions for
EPA’s approval in the Pennsylvania SIP
under 40 CFR 52.2020(d)(1). The RACT
II permits submitted by PADEP are
listed in the last column of Table 1 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–2020–0189.3 EPA is
incorporating by reference in the
Pennsylvania SIP, via the RACT II
permits, source-specific RACT emission
limits and control measures under the
1997 and 2008 8-hour ozone NAAQS for
certain major sources of NOX and VOC
emissions.
B. EPA’s Proposed Action
PADEP’s SIP revisions incorporate its
determinations of source-specific RACT
II controls for individual emission units
at major sources of NOX and/or VOC in
Pennsylvania, where those units are not
covered by or cannot meet
Pennsylvania’s presumptive RACT
regulation. After thorough review and
evaluation of the information provided
by PADEP in its five SIP revision
submittals for four major sources of NOX
and/or VOC in Pennsylvania, EPA
proposed to find that PADEP’s case-bycase RACT determinations and
conclusions establish limits and/or
controls on individual sources that are
reasonable and appropriately
considered technically and
economically feasible controls.
PADEP, in its RACT II
determinations, considered the prior
source-specific RACT I requirements
and, where more stringent, retained
those RACT I requirements as part of its
new RACT determinations. In the
NPRM, EPA proposed to find that all the
proposed revisions to previously SIP
approved RACT I requirements would
result in equivalent or additional
reductions of NOX and/or VOC
emissions. The proposed revisions
should not interfere with any applicable
requirement concerning attainment or
reasonable further progress with the
NAAQS or interfere with other
applicable CAA requirements in section
110(l) of the CAA.
Other specific requirements of
Pennsylvania’s 1997 and 2008 8-hour
ozone NAAQS case-by-case RACT
determinations and the rationale for
EPA’s proposed action were explained
in the NPRM and its associated
technical support document (TSD) and
will not be restated here.
2 While the prior SIP-approved RACT I permit
will remain part of the SIP, this RACT II rule will
incorporate by reference the RACT II requirements
through the RACT II permit and clarify the ongoing
applicability of specific conditions in the RACT I
permit.
3 The RACT II permits are redacted versions of a
facility’s Federally enforceable permits and reflect
the specific RACT requirements being approved
into the Pennsylvania SIP.
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III. Public Comments and EPA
Responses
EPA received comments from seven
commenters on the May 5, 2020 NPRM.
85 FR 26647. A summary of the
comments and EPA’s response are
discussed in this section of the
preamble. A copy of the comments can
be found in the docket for this rule.
Comment 1: The commenter states
that water/steam injection is a control
option for Transco Station 520’s simple
cycle turbines that was inappropriately
determined to be technically infeasible
and indicates that this control option is
found on EPA’s RACT/BACT/LAER
Clearinghouse (RBLC) as technically
feasible in at least 10 natural gas fired
simple cycle turbines over the last 20
years. The commenter further states that
EPA had made a similar comment for
the public record on the technical
feasibility of water/steam injection and
had arbitrarily reversed its position in
the NPRM. The commenter claims that
the reasons given for technical
infeasibility such as water/steam
supply, storage tanks, the source of
water, and water treatment and
pretreatment are economic, and not
technical, feasibility issues. For these
reasons, the commenter states that EPA
should disapprove PADEP’s RACT
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determination for Transco Station 520
and reevaluate the economic feasibility
of water/steam injection.
Response 1: The commenter is correct
in stating that EPA made prior
comments suggesting that water/steam
injection was a technically feasible
control option for natural gas fired
simple cycle turbines in gas
transmission service that should be
evaluated for economic feasibility.
However, EPA disagrees that it has
arbitrarily changed its position in
proposing to approve the case-by-case
RACT requirements for the two Transco
Station 520 simple cycle turbines. Both
the facility and PADEP responded to
EPA’s comment explaining why the
water/steam injection control option
was not technically feasible at this
specific site.
PADEP conducted its case-by-case
RACT analysis of potential controls for
Transco’s natural gas fired simple cycle
turbines pursuant to the requirements of
Pennsylvania’s RACT regulations. The
case-by-case RACT II analysis
requirements are set forth in 25 PA Code
129.99(c), which then references the
RACT proposal requirements identified
in 25 Pa Code 129.92. As identified in
Section 129.92(b)(1), ‘‘[a]vailable control
options are air pollution control
technologies with a reasonable potential
for application at the source.’’ Section
129.29(b)(2) further identifies that ‘‘[a]
determination of technical infeasibility
shall identify technical difficulties
which would preclude the successful
use of the control option on the source.’’
The water/steam injection control
option requires a large volume of
purified water. The Transco facility is
located in a remote location without a
viable on-site source of clean water. In
order to have the needed purified water
on-site for water/steam injection,
Transco would need to drill an on-site
well or transport water to an on-site
water purification facility. A water
study would be needed to determine
whether and how an on-site well could
be drilled. Transporting water to the site
would require the installation of a water
purification facility and large on-site
storage tanks. The need to transport
water to the site for the use of water/
steam injection also introduces
unreliability and the risk of insufficient
water due to the unpredictable nature of
weather and transportation. The
uncertainties created by the need to
transport water to the site increases the
risk of system failure because the
Transco turbines are peaking units.
Given the nature of peak demand, these
turbines are required to operate
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immediately when necessary with little
advanced notice.4
For these reasons, the RACT analysis
determined that water/steam injection
was technically infeasible for the
Transco turbines. Lacking an on-site
water source or a reliable off-site source
of on-demand water, it was reasonable
for PADEP to conclude that water/steam
injection was not an available control
option with a ‘‘reasonable potential
application at the source.’’ While the
need to install a water purification
system and large on-site storage tanks
may be factors that can be evaluated
through an economic feasibility
analysis, the lack of an on-site water
source and the risks and uncertainties of
an insufficient water supply due to the
potential need for the on-demand
trucking of water are issues far more
fundamental to determining initially
whether using water/steam injection is
truly an available control technology for
these sources at this site. These
circumstances present ‘‘technical
difficulties which would preclude the
successful use of the control option on
the affected source.’’ After reviewing the
responses from the company and
PADEP, EPA concluded that PADEP’s
RACT determination that water/steam
injection is not technically feasible for
the Transco Station 520 peaking
turbines was a reasonable conclusion
based on Pennsylvania’s RACT
requirements.
Comment 2: The commenter
complains that the Transco Station 520
redacted permit consists of non-uniform
pages, where one added page is in color
and the remaining pages are in black
and white. The commenter claims that
EPA illegally altered the state’s
submittal to correct a mistake made by
the state. The commenter refers to a
prior proposed rulemaking, EPA–R03–
OAR–2017–0290, where the redacted
permit for Transco station 520, included
in the docket for that proposed
rulemaking, did not include the 79.3
lbs/hr and 95.6 tpy RACT emission
limits. However, the commenter notes
that the redacted permit in the current
docket does contain such RACT limits.
The commenter states that EPA must
remit the SIP back to Pennsylvania to
incorporate enforceable RACT
limitations.
Response 2: The commenter’s concern
relates to the RACT emission limits for
Source ID 106 in the Transco Station
520 Permit No. 41–00001, Section D, I.,
Condition #004. The commenter notes
4 See email dated May 18, 2017 from Williams to
PADEP and PADEP memorandum dated May 22,
2017, which are both part of the record for this
docket.
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66259
that, in a proposed rule from 2017,
EPA–R03–OAR–2017–0290 which was
never finalized, this permit condition
was not included in the redacted permit
to be incorporated into the SIP.5 This
was an inadvertent error because the
emission limits contained in the permit
condition were always intended to be
part of Pennsylvania’s RACT
determination for this source. See, for
example, the PADEP technical review
memo, dated February 22, 2017, the
EPA TSD, and the full Transco Station
520 Permit No. 41–00001, all of which
were in the docket for the 2017
proposed action. EPA, subsequently
notified PADEP that the SIP submittal
for Transco Station 520 contained an
incorrectly redacted permit. On April 6,
2020, PADEP supplemented their SIP
submittal with the correctly redacted
permit.6 The docket for the proposal for
the current rulemaking included a
correctly redacted permit, which
included the 79.3 lbs/hr and 95.6 tpy
RACT emission limits.7
Comment 3: The commenter agrees
with EPA’s proposed approval of
PADEP’s determination to avoid the use
of the blowing agent 152a when
considering RACT alternatives to the
use of pentane. The commenter explains
that coal is not the only substance that
is bad for the environment and claims
that blowing agent 152a is an extremely
dangerous compound that is harmful to
the environment because it is a potent
greenhouse gas, a carcinogen and
produces carbon dioxide.
Response 3: While the commenter
does not identify a specific facility, we
believe the commenter’s comment
applies to the Novipax facility, where
the blowing agent 152a was discussed in
the RACT analysis. EPA appreciates the
support of the commenter for the
Novipax RACT determination.
5 EPA never took any final action under the EPA–
R03–OAR–2017–0290 proposed rulemaking
because of CBI issues with the docket. See
discussion in Supplementary Information section of
this preamble.
6 PADEP supplemented its SIP revision submittal
with a corrected version of the redacted permits for
Transco via email on April 6, 2020. The revised
redacted permit was appropriately added to the
supporting materials for the current proposed
rulemaking. The email from PADEP to EPA Region
3, dated April 6, 2020, is now being added to the
final docket along with the Final Rule Notice.
7 EPA notes that PADEP, in its RACT SIP
revisions for Transco Station 520, Novipax, SPTM,
and Global Advanced Metals, included some form
of annual limits in the RACT II permits for those
facilities. EPA wishes to clarify that it is not
approving any such annual limits as RACT limits.
Rather, because PADEP analyzed what should be
RACT under operating conditions that included
annual limits from the existing facility permit, and
PADEP included those requirements in its SIP
submittal to us, EPA is incorporating those annual
limits into the SIP not as RACT control limits but
for the purpose of SIP strengthening.
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Comment 4: The commenter states
that EPA should require more controls
for Sunoco Partners Marketing and
Terminals (SPMT), including controls
that exceed Pennsylvania’s cost
thresholds of $2,800/ton or other states’
$5,000/ton cost thresholds. The
commenter claims that facilities such as
SPMT, which causes millions of dollars
in environmental damage and makes
millions of dollars, can afford to do
more and should be required to do
more. The commenter explains that the
area in which SPMT is located is
historically poor, damaged by industrial
pollution, and is a neighborhood of
black and brown people. The
commenter claims that EPA has a duty
to consider environmental justice and
should disapprove the RACT
determination for SPMT and require
PADEP to use a higher cost threshold
and force RACT level controls to be
installed.
Response 4: There are seven emission
units that required case-by-case RACT
determinations at the SPMT facility.
The RACT determinations are governed
by the requirements of 25 Pa. Code
129.99, which requires a technical and
economic feasibility analysis of
available control options. Three of these
emission units are the auxiliary boilers.
The SPMT auxiliary boilers are dualfueled, burning both natural gas and
refinery gas. They are currently
controlled with low NOX burners and
flue gas recirculation. PADEP’s case-bycase RACT II determination require
these boilers to achieve a 0.05 lb NOX/
MMBtu emission limit, which will be
incorporated into the SIP through the
current rule. This new limit tightens the
prior RACT I limit of 0.25 lb NOX/
MMBtu emission limit. Although there
are no presumptive RACT requirements
that apply to SPMT’s dual-fired boilers,
the RACT II limit of 0.05 lb NOX/
MMBtu is at least twice as stringent as
the presumptive RACT requirements at
25 Pa. Code 129.97(g)(1) for combustion
units equal to or greater than 50 MMBtu
heat input. Because the SPMT boilers
are already controlled and achieve
relatively low NOX emissions,
additional controls were found to be
economically infeasible. The cost
effectiveness evaluation of the
technically feasible control options for
these boilers determined a range of costs
from $12,126 to $52,331/ton of NOX
reduced, a cost level well above the
higher $5,000 cost threshold identified
by the commenter.8
8 See Sunoco Partners Marketing and Terminals,
L.P., RACT II Proposal, Philadelphia, Pennsylvania,
dated November 2016.
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The fourth emission unit subject to
case-by-case RACT is the marine vessel
loading operation that is currently
subject to the requirements of 25 Pa.
Code § 129.81 and 40 CFR part 63,
subpart Y, the National Emission
Standards for Marine Tank Vessel
Loading Operations, which contains
additional requirements for vapor
collection and leak detection. All
marine vessel loading at the facility is
currently controlled by a marine vapor
recovery (MVR) system which captures
gases and directs them to the fuel gas
system to be combusted as a fuel in the
auxiliary boilers. The RACT analysis of
the marine vessel loading operations
concluded that there is no feasible
control with a greater control efficiency
than the current MVR control
technology. Because there were no
technically feasible controls better than
the current controls, a cost effectiveness
analysis was not required.9
The fifth emission unit subject to
case-by-case RACT is a single cooling
tower, which has a potential to emit 4.6
tpy VOC. There were no technically or
economically feasible control options
for this source in addition to what is
already required under prior RACT SIP
approvals, which are equipment
inspection and monitoring.10 The sixth
and seventh emission units subject to
case-by-case RACT are fugitive leaks
from valves and fugitive leaks across the
facility. Again, the RACT analysis
identified that there were no technically
feasible controls for these sources. For
both of these sources, PADEP is
requiring as RACT compliance with 40
CFR part 60 subpart VV, Standards of
Performance for Equipment Leaks of
VOC in the Synthetic Organic
Chemicals Manufacturing Industry (or
VVa as appropriate), which minimizes
leaks from valves, flanges, and tanks
through the use of specified equipment,
work practices and inspections.11
As identified in this preamble, PADEP
followed the RACT analysis
requirements of 25 Pa. Code 129.99 and
for only three sources was it able to
identify additional technically feasible
control options. For those sources, the
three auxiliary boilers, the cost of added
emission reduction well exceeded even
the higher cost effectiveness threshold
identified by the commenter. In its
approval capacity, EPA shall approve a
state’s proposed RACT proposal if it
meets the statutory and regulatory
requirements of the program. CAA
Section 110(k)(3). In this case, EPA
determined that PADEP’s proposed
9 Id.
RACT SIP was reasonable and met the
statutory and regulatory requirements.
The commenter also urges EPA to
consider environmental justice as part
of the RACT determination for this
facility. 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 determining RACT are
those in the statue and regulations, and
environmental justice is not a statutory
or regulatory factor in the RACT
analysis. As described in this preamble
and in our proposal document we
believe it is appropriate to fully approve
PADEP’s SIP submittal with respect to
RACT for SPMT.
Comment 5: One commenter asserts
that ‘‘other neighboring states such as
New York and New Jersey both have
cost effectiveness thresholds set at or
above $5,000 per ton, but here EPA
arbitrarily allows a lower dollar per ton
threshold!’’ The commenter goes on to
question EPA’s approval of a lower cost
threshold in Pennsylvania. Further, the
commenter states that ‘‘EPA must retract
their proposed approval and set a
uniform dollar per ton threshold based
on, and consistent with, past EPA
actions’’ and ‘‘that the cost per ton
threshold should at least be consistent
in the Ozone Transport Region (OTR).’’
Lastly, the commenter claims that ‘‘EPA
is arbitrary and capricious when
approving two different states RACT
SIPs with inconsistent cost thresholds’’
and that ‘‘EPA needs to set the bar, not
let the states waffle in the wind and
never install controls.’’
Response 5: EPA is aware that
Pennsylvania considered costeffectiveness levels ($/ton removed) that
are lower than other states, such as New
Jersey and New York as the commenter
notes, when developing the RACT II
rule. However, EPA has not set a single
cost, emission reduction, or costeffectiveness figure to fully define costeffectiveness in meeting the NOX or
VOC RACT requirement. Therefore,
states have the discretion to determine
what costs are considered reasonable
when establishing RACT for their
sources. Each state must make and
defend its own determination on how to
weigh these values in establishing
RACT.
As PADEP explained in its RACT II
rulemaking, it did not establish a brightline cost effectiveness threshold in
determining what is economically
reasonably for purposes of defining
RACT.12 Instead, it developed as
guidance a cost-effectiveness threshold
10 Id.
11 Id.
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of $2,800 per ton of NOX controlled and
$5,500 per ton of VOC controlled for
RACT. Pennsylvania also determined
that even evaluating control technology
options with an additional 25% margin,
an upper bound cost-effectiveness
threshold of $3,500 per ton NOX
controlled and $7,000 per ton VOC
controlled, would not affect the add-on
control technology decisions required
by RACT. Id. Pennsylvania determined
that these higher cost-effectiveness
thresholds did not impact the
determination of what add on control
technology was feasible. Pennsylvania
also reviewed examples of benchmarks
used by other states: Wisconsin, $2,500
per ton NOX; Illinois, $2,500–$3,000 per
ton NOX; Maryland, $3,500–$5,000 per
ton NOX; Ohio, $5,000 per ton NOX; and
New York, $5,000–$5,500 per ton
NOX.13
In a separate prior final agency action,
EPA found that PADEP’s cost
effectiveness thresholds are reasonable
and reflect control levels achieved by
the application and consideration of
available control technologies, after
considering both the economic and
technological circumstances of
Pennsylvania’s own sources. See 84 FR
20274, 20286 (May 9, 2019).
Comment 6: The commenter notes
that good operating practices are
determined to be RACT for several
sources at Global Advanced Metals.
However, the commenter claims that for
Source IDs 102, 124, and 201, those
good operating practices are not defined
in the permit.
Response 6: The commenter is
correct, in part, in stating that good
operating practices have been
determined as VOC RACT for Source
IDs 102, 124, and 201. However, they
are only one aspect of the overall RACT
II requirements imposed on the sources.
For all three sources, PADEP conducted
a VOC RACT analysis per 25 Pa. Code
129.99, concluding that the additional
control technologies evaluated were
either technically and/or economically
infeasible and that RACT would, among
other requirements, be operation and
maintenance of the source in
accordance with manufacturers’
specifications and good air pollution
control practices.14
13 PADEP Responses to Frequently Asked
Questions, Final Rulemaking RACT Requirements
for Major Sources of NOX and VOCs. October 20,
2016.
14 This identical permit condition can be found in
Global Advanced Metals’ redacted Permit No. 46–
00037, Section D, Source 102, VI. Condition #013;
Source ID 124, VI. Condition #010; and Source ID
201, I. Condition #002, which is part of the record
of this docket and will be incorporated into the SIP
through this action.
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As noted previously, PADEP imposed
additional RACT requirements on these
sources based on existing permit
conditions, which were considered in
the RACT analysis. For instance, Global
Advanced Metals currently utilizes a
recovery unit to control methyl isobutyl
ketone (MIBK) emissions from Source
ID 124, the extraction process in
Building 74, and PADEP has imposed
the requirement to operate this recovery
unit as a RACT requirement. The RACT
II permit also includes efficiency
restrictions on the control device and
extensive recordkeeping requirements
on operational factors such as flow
rates, pressure drops, MIBK content in
influent and effluent, and maintenance
downtime.15
The MIBK recovery system also helps
to limit emissions from Source ID 102,
the tantalum salts process in Building
19.16 While the RACT II permit does not
specifically include the operation of the
MIBK recovery unit for Source 102, the
recovery unit’s operation is required in
the RACT II permit under Source 124,
as identified in this preamble. PADEP
also imposed on Source 102 a
throughput restriction on the number of
batches.17 Additionally, the RACT II for
Source ID 201, the wastewater treatment
plant, included a requirement to
provide PADEP with relevant records
found in the facility’s National Pollutant
Discharge Elimination System (NPDES)
permit, upon request.18
EPA concluded that ‘‘good operating
practices,’’ which was determined as
VOC RACT for these three sources by
PADEP, is adequately defined in the
facility’s permit as ‘‘operating and
maintaining the source in accordance
with manufacturers’ specifications.’’
The requirement to operate the source
in accordance with the manufacturer’s
specifications holds the facility
accountable for operating and
maintaining each of these three sources
per the guidance established by the
manufacturer specifically for that
particular source. The good operating
15 See Global Advanced Metals’ redacted Permit
No. 46–00037, Section D, Source ID 124, I.
Condition #003 and IV. Conditions #006, #007 and
#010; which is part of the record of this docket and
will be incorporated into the SIP through this
action.
16 See Global Advanced Metals’ Alternative RACT
Compliance proposal, dated October 2016, which is
part of the record for this docket.
17 See Global Advanced Metals’ redacted Permit
No. 46–00037, Section D, Source 102, I. Conditions
#004, which is part of the record for this docket and
will be incorporated into the SIP through this
action.
18 See Global Advanced Metals’ redacted Permit
No. 46–00037, Section D, Source ID 201, I.
Condition #001, which is part of the record for this
docket and will be incorporated into the SIP
through this action.
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66261
practices requirement is further clarified
and strengthened by the additional
RACT requirements for recovery unit
operation, operational restrictions, and
recordkeeping included in the redacted
permit to be incorporated into the SIP.
Comment 7: The commenter notes
that EPA is approving particulate matter
(PM) limits for Global Advanced Metals
as part of the facility’s RACT
determination. The commenter asks
why and what relationship these PM
limits have in setting NOX and/or VOC
RACT emission limits for the source.
Response 7: While the commenter
does not provide a specific reference to
the PM limits in question, EPA assumes
the commenter is referring to the PM
limit of ‘‘not to exceed 0.02 grains per
dry standard cubic foot’’ as a control
device efficiency restriction for the
RotoClone wet dust collector.19 The
RotoClone wet dust collector was not
one of the control technologies
examined by PADEP for the control of
VOCs from Source 109. Rather, it is a
control technology for PM. The PM
limits were established under other
regulatory programs and not the RACT
program. It was identified as an ongoing
facility requirement while reviewing the
VOC RACT requirements for the fugitive
emissions from ethanol transfer and
storage operations. The commenter’s
concern about PM is warranted. The PM
limits are not included in the source’s
permit to address RACT requirements
and therefore should not be
incorporated into the SIP through the
current rule. PADEP has subsequently
submitted a revised redacted permit that
does not include the PM requirements
for incorporation into the SIP.20
Comment 8: The commenter notes
that for Source ID 201 at Global
Advanced Metals, the RACT
determination includes the submission
of records required under the facility’s
NPDES permit. The commenter claims
that neither EPA nor PADEP provide
justification or explanation as to why
submission of these records is
necessary. The commenter claims that
EPA has no authority under the CAA to
require submission of records under the
Clean Water Act (CWA), stating that the
19 Global Advanced Metals’ redacted Permit No.
46–00037, Section D., Source ID 109, Condition
#003(b)(2).
20 See August 21, 2020 email from PADEP to EPA
identifying changes to redacted RACT II permit for
Global Advanced Metals and attaching the revised
redacted permit. Both documents have been added
to the docket in this matter and the revised redacted
permit will be incorporated into the SIP. At the
same time, PADEP has also revised the original
RACT II permit by deleting requirements for Source
102 related to hydrogen flouride and hydrogen
chloride for similar reasons. Those facility
requirements were not related to VOC control.
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Information Collection Request (ICR)
approved for these records makes no
mention of allowing them to be used for
purposes outside of the NPDES
program. The commenter claims that in
order for EPA to require submission of
these records for CAA purposes, EPA
would have to go through the ICR
process and calculate the burden on
these sources to do so.
Response 8: The commenter is correct
that among the RACT requirements for
Source ID 201, the wastewater treatment
plant (WWTP), Condition #001 requires
the facility to ‘‘provide to the DEP, upon
request, copies of records required by
the NPDES permit.’’ 21 This condition is
determined to be part of the source’s
VOC RACT determination per 25 Pa.
Code 129.100(d).
EPA disagrees with the commenter
that there is insufficient justification or
explanation as to why these records are
relevant to the VOC RACT
determination for the WWTP. In its VOC
RACT analysis, PADEP explained that
the constituents of the wastewater at
Global Advanced Metals include
dissolved VOCs, which may be emitted
to some extent to the atmosphere in the
treatment process.22 Knowledge of the
wastewater constituents informs
PADEP’s knowledge as to the
effectiveness of the wastewater
treatment process in removing VOC
emissions at this source. Information on
such constituents is contained in the
regular testing of total suspended solids
and total dissolved solids performed by
Global Advanced Metals pursuant to its
NPDES permit. Therefore, this
information is directly related to the
control of VOC air emissions from the
WWTP.
EPA also disagrees with the
commenter’s contentions about the use
of NPDES records for RACT purposes
and believes the commenter may have
misinterpreted the nature of EPA’s
proposed action. In this SIP action, EPA
is not relying on any CWA information
collection authorization and is not
adding such into the SIP. Rather, it is
approving a legitimate permit term
established by PADEP, under its own
independent authority (the Air
Pollution Control Act) to collect air
emissions data, into the Pennsylvania
SIP. Data that is collected under the
NPDES program related to dissolved
VOC constituents in a facility’s
wastewater is such data and referring to
the NPDES permit merely helps the
21 Global Advanced Metals’ redacted Permit No.
46–00037, Section D, Source ID 201, Condition
#001.
22 See PADEP’s technical review memo, dated
March 6, 2017, which is included as part of the
docket for this action.
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16:28 Oct 16, 2020
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facility identify the required data but is
not the authority being used to collect
it. The reference to the NPDES permit
helps to identify that the information
needed to be supplied for compliance
with the Pennsylvania air permit is the
same as the information being collected
under the CWA. It is merely a
convenient way of identifying the data
needed to be reported under the air
permit and is not the basis for the state’s
authority to include it in the permit.
IV. Final Action
EPA is approving case-by-case RACT
determinations for four sources in
Pennsylvania, as required to meet
obligations pursuant to the 1997 and
2008 8-hour ozone NAAQS, as revisions
to the Pennsylvania SIP.
V. Incorporation by Reference
In this document, EPA is finalizing
regulatory text that includes
incorporation by reference. In
accordance with requirements of 1 CFR
51.5, EPA is finalizing the incorporation
by reference of source-specific RACT
determinations under the 1997 and 2008
8-hour ozone NAAQS for certain major
sources of VOC and NOX in
Pennsylvania. EPA has made, and will
continue to make, these materials
generally available through https://
www.regulations.gov and at the EPA
Region III Office (please contact the
person identified in the FOR FURTHER
INFORMATION CONTACT section of this
preamble for more information).
Therefore, these materials have been
approved by EPA for inclusion in the
SIP, have been incorporated by
reference by EPA into that plan, are
fully Federally enforceable under
sections 110 and 113 of the CAA as of
the effective date of the final rule of
EPA’s approval, and will be
incorporated by reference in the next
update to the SIP compilation.23
VI. Statutory and Executive Order
Reviews
A. General Requirements
Under the CAA, the Administrator is
required to approve a SIP submission
that complies with the provisions of the
CAA and applicable Federal regulations.
42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions,
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this action
merely approves state law as meeting
Federal requirements and does not
impose additional requirements beyond
those imposed by state law. For that
reason, this action:
23 62
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Frm 00062
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• 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);
• Is not an Executive Order 13771 (82
FR 9339, February 2, 2017) regulatory
action because it is not a significant
regulatory action under Executive Order
12866.
• 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
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Congress and to the Comptroller General
of the United States. Section 804,
however, exempts from section 801 the
following types of rules: Rules of
particular applicability; rules relating to
agency management or personnel; and
rules of agency organization, procedure,
or practice that do not substantially
affect the rights or obligations of nonagency parties. 5 U.S.C. 804(3). Because
this is a rule of particular applicability,
EPA is not required to submit a rule
report regarding this action under
section 801.
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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 December 18, 2020. 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 four case-by-
case facilities for the 1997 and 2008 8hour 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: September 22, 2020.
Cosmo Servidio,
Regional Administrator, Region III.
40 CFR part 52 is amended as follows:
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
66263
a. Revising the entries ‘‘W.R. Grace
and Co.—FORMPAC Div’’; ‘‘ W. R.
Grace and Co.—Reading Plant’’; ‘‘Cabot
Performance Materials—Boyertown’’;
‘‘Sunoco, Inc. (R&M); Marcus Hook
Plant’’; and ‘‘Transcontinental Gas
Pipeline Corporation’’ (Permit No. PA–
41–0005A); and
■ b. Adding the following entries at the
end of the table: ‘‘Transco—
Salladasburg Station 520 (formerly
referenced as Transcontinental Gas
Pipeline Corporation)’’; ‘‘Novipax
(formerly referenced as W. R. Grace and
Co.—FORMPAC Div and W. R. Grace
and Co.—Reading Plant)’’; ‘‘Sunoco
Partners Marketing & Terminals
(formerly referenced as Sunoco, Inc.
(R&M); Marcus Hook Plant)’’; and
‘‘Global Advanced Metals USA, Inc.
(formerly referenced as Cabot
Performance Materials—Boyertown)’’.
The revisions and additions read as
follows:
■
§ 52.2020
*
2. In § 52.2020, the table in paragraph
(d)(1) is amended by:
■
Identification of plan.
*
*
(d) * * *
(1) * * *
*
*
Additional
explanations/
§§ 52.2063 and
52.2064
citations 1
Name of source
Permit No.
County
State effective
date
*
*
W. R. Grace and Co.—FORMPAC Div ............
*
PA–06–1036 ..
*
Berks .............
*
5/12/95 ...........
*
5/16/96, 61 FR 24706
W. R. Grace and Co.—Reading Plant .............
PA–06–315–
001.
Berks .............
6/4/92 .............
5/16/96, 61 FR 24707
*
*
Cabot Performance Materials—Boyertown ......
*
OP–46–0037
*
Montgomery ...
*
4/13/99 ...........
*
12/15/00, 65 FR 78418
*
See also
52.2064(b)(4).
*
*
Sunoco, Inc. (R&M); Marcus Hook Plant .........
*
CP–23–0001 ..
*
Delaware .......
*
6/8/95, 8/2/01
*
10/30/01, 66 FR 54699
*
See also
52.2064(b)(3).
*
*
Transcontinental Gas Pipeline Corporation .....
*
PA–41–0005A
*
Lycoming .......
*
8/9/95 .............
*
8/24/05, 70 FR 49496
*
See also
52.2064(b)(1).
*
*
Transco—Salladasburg Station 520 (formerly
referenced as Transcontinental Gas Pipeline
Corporation).
*
41–00001 .......
*
Lycoming .......
*
6/6/17 .............
*
52.2064(b)(1).
Novipax (formerly referenced as W. R. Grace
and Co.—FORMPAC Div and W. R. Grace
and Co.—Reading Plant).
06–05036 .......
Berks .............
12/19/17 .........
Sunoco Partners Marketing & Terminals (formerly referenced as Sunoco, Inc. (R&M);
Marcus Hook Plant).
23–00119 .......
Delaware .......
1/20/17 ...........
*
October 19, 2020, [INSERT FEDERAL
REGISTER CITATION].
October 19, 2020, [INSERT FEDERAL
REGISTER CITATION].
October 19, 2020, [INSERT FEDERAL
REGISTER CITATION].
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EPA approval date
E:\FR\FM\19OCR1.SGM
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*
See also
52.2064(b)(2).
See also
52.2064(b)(2).
52.2064(b)(2).
52.2064(b)(3).
66264
Federal Register / Vol. 85, No. 202 / Monday, October 19, 2020 / Rules and Regulations
Name of source
Permit No.
County
State effective
date
Global Advanced Metals USA, Inc. (formerly
reference as Cabot Performance Materials—Boyertown).
46–00037 .......
Montgomery ...
3/10/17 ...........
1 The
October 19, 2020, [INSERT FEDERAL
REGISTER CITATION].
52.2064(b)(4).
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 (b) 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).
*
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EPA approval date
Additional
explanations/
§§ 52.2063 and
52.2064
citations 1
*
*
*
*
(b) Approval of source-specific RACT
requirements for 1997 and 2008 8-hour
ozone national ambient air quality
standards for the facilities listed below
are incorporated as specified below.
(Rulemaking Docket No. EPA–OAR–
2020–0189).
(1) Transco—Salladasburg Station
520—Incorporating by reference Permit
No. 41–00001, issued June 6, 2017, as
redacted by Pennsylvania, which
supersedes the prior RACT Permit No.
41–0005A, issued August 9, 1995,
except for Conditions 3, 4, 6, 8, 14, and
18, which remain as RACT requirements
applicable to the three 2050 hp Ingersoll
Rand engines #1, 2, and 3 (Source IDs
P101, P102, P103). See also
§ 52.2063(d)(1)(i) for prior RACT
approval.
(2) Novipax—Incorporating by
reference Permit No. 06–05036, issued
December 19, 2017, as redacted by
Pennsylvania, which supersedes the
prior RACT Plan Approval No. 06–1036,
issued May 12, 1995 to W. R. Grace and
Co. FORMPAC Division, except for
Conditions 3, 4 (applicable to two
pentane storage tanks, Source IDs 101
and 101A), 5 (applicable to extruders,
Source ID 102, and facility wide to
Source IDs 103, 104, 105, 106, 106B,
106C, 107, and 108), 7 (applicable to
Source IDs 101, 101A, and 102) and 8
(applicable to Source IDs 101, 101A,
and 102), which remain as RACT
requirements applicable to the indicated
sources, and Plan Approval No. 06–
315–001, issued June 4, 1992 to W. R.
Grace and Co.—Reading Plant, except
for Conditions 4 (applicable to Source
ID 102), 5 (applicable to Source IDs 101
and 101A), and 6 (applicable to Source
IDs 101, 101A, and 102), which remain
as RACT requirements applicable to the
indicated sources. See also
§ 52.2063(c)(108)(i)(B)(6) for prior RACT
approvals.
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16:28 Oct 16, 2020
Jkt 253001
(3) Sunoco Partners Marketing &
Terminals—Incorporating by reference
Permit No. 23–00119, issued January 20,
2017, as redacted by Pennsylvania,
which supersedes the prior RACT
Compliance Permit No. CP–23–0001,
issued June 8, 1995 and amended on
August 2, 2001, except for Conditions
5E (applicable to diesel engine and
stormwater pumps, Source ID 113), 6A
(applicable to marine vessel loading,
Source ID 115), 6B (tank truck loading),
6C (applicable to cooling tower 15–2B,
Source ID 139), and 6D (applicable to
waste water treatment, Source 701),
which remain as RACT requirements
applicable to the indicated sources. See
also § 52.2063(c)(179)(i)(B)(6) for prior
RACT approval.
(4) Global Advanced Metals USA,
Inc.—Incorporating by reference Permit
No. 46–00037, issued March 10, 2017,
as redacted by Pennsylvania, which
supersedes the prior RACT Permit No.
OP–46–0037, issued April 13, 1999,
except for condition 15, which remains
as a RACT requirement applicable to the
tantalum salts process (Source ID 102),
the extraction process (Source ID 124),
the wastewater treatment plant (Source
ID 201), and fugitive emissions from
ethanol transfer and storage (Source
109). See also § 52.2063(c)(143)(i)(B)(20)
for prior RACT approval.
[FR Doc. 2020–21438 Filed 10–16–20; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R07–OAR–2020–0356; FRL–10015–
03–Region 7]
Air Plan Approval; Missouri; Removal
of Control of Emissions From
Polyethylene Bag Sealing Operations
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
The Environmental Protection
Agency (EPA) is taking final action to
approve a revision to the State
Implementation Plan (SIP) submitted by
SUMMARY:
PO 00000
Frm 00064
Fmt 4700
Sfmt 4700
the State of Missouri on January 15,
2019, and supplemented by letter on
July 11, 2019. In the proposal, EPA
proposed removal of a rule related to the
control of emissions from polyethylene
bag sealing operations in the St. Louis,
Missouri area from its SIP. This removal
does not have an adverse effect on air
quality. The EPA’s approval of this rule
revision is in accordance with the
requirements of the Clean Air Act
(CAA).
This final rule is effective on
November 18, 2020.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. EPA–R07–OAR–2020–0356. 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, i.e., 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 information.
FOR FURTHER INFORMATION CONTACT:
David Peter, Environmental Protection
Agency, Region 7 Office, Air Permitting
and Standards Branch, 11201 Renner
Boulevard, Lenexa, Kansas 66219;
telephone number: (913) 551–7397;
email address: peter.david@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document ‘‘we,’’ ‘‘us,’’
and ‘‘our’’ refer to the EPA.
DATES:
Table of Contents
I. What is being addressed in this document?
II. Have the requirements for approval of a
SIP revision been met?
III. What action is the EPA taking?
IV. Incorporation by Reference
V. Statutory and Executive Order Reviews
I. What is being addressed in this
document?
The EPA is approving the removal of
10 Code of State Regulation (CSR) 10–
E:\FR\FM\19OCR1.SGM
19OCR1
Agencies
[Federal Register Volume 85, Number 202 (Monday, October 19, 2020)]
[Rules and Regulations]
[Pages 66257-66264]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2020-21438]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R03-OAR-2020-0189; FRL-10014-98-Region 3]
Approval and Promulgation of Air Quality Implementation Plans;
Pennsylvania; Reasonably Available Control Technology (RACT)
Determinations for Case-by-Case Sources Under the 1997 and 2008 8-Hour
Ozone National Ambient Air Quality Standards
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
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SUMMARY: The Environmental Protection Agency (EPA) is approving
multiple state implementation plan (SIP) revisions submitted by the
Commonwealth of Pennsylvania. These revisions were submitted by the
Pennsylvania Department of Environmental Protection (PADEP) to
establish and require reasonably available control technology (RACT)
for 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 action,
EPA is only approving source-specific (also referred to as ``case-by-
case'') RACT determinations for four major sources. These RACT
evaluations were submitted to meet RACT requirements for the 1997 and
2008 8-hour ozone national ambient air quality standards (NAAQS). EPA
is approving these revisions to the Pennsylvania SIP in accordance with
the requirements of the Clean Air Act (CAA) and EPA's implementing
regulations.
DATES: This final rule is effective on November 18, 2020.
ADDRESSES: EPA has established a docket for this action under Docket ID
Number EPA-R03-OAR-2020-0189. All documents in the docket are listed on
the https://www.regulations.gov website. Although listed in the index,
some information is not publicly available, e.g., confidential business
information (CBI) or other information whose disclosure is restricted
by statute. Certain other material, such as copyrighted material, is
not placed on the internet and will be publicly available only in hard
copy form. Publicly available docket materials are available through
https://www.regulations.gov, or please contact the person identified in
the For Further Information Contact section for additional availability
information.
FOR FURTHER INFORMATION CONTACT: Ms. Emily Bertram, Permits Branch
(3AD10), Air & Radiation Division, U.S. Environmental Protection
Agency, Region III, 1650 Arch Street, Philadelphia, Pennsylvania 19103.
The telephone number is (215) 814-5273. Ms. Bertram can also be reached
via electronic mail at [email protected].
SUPPLEMENTARY INFORMATION:
I. Background
On May 5, 2020, EPA published a notice of proposed rulemaking
(NPRM). 85 FR 26647. In the NPRM, EPA proposed approval of case-by-case
RACT determinations for four sources in Pennsylvania for the 1997 and
2008 8-hour ozone NAAQS. The case-by-case RACT determinations for these
four sources were included in SIP revisions submitted by PADEP on
November 21, 2017, April 26, 2018, June 26, 2018, and October 29, 2018.
Under certain circumstances, states are required to submit SIP
revisions to address RACT requirements for major sources of
NOX and VOC or any source category for which EPA has
promulgated control technique guidelines (CTG) for each ozone NAAQS.
Which NOX and VOC sources in Pennsylvania are considered
``major,'' and therefore to be addressed for RACT revisions, is
dependent on the location of each source within the Commonwealth.
Sources located in nonattainment areas would be subject to the ``major
source'' definitions established under the CAA based on their
classification. In the case of Pennsylvania, sources located in any
areas outside of moderate or above nonattainment areas, as part of the
Ozone Transport Region (OTR), are subject to source thresholds of 50
tons per year (tpy). CAA section 184(b).
On May 16, 2016, PADEP submitted a SIP revision addressing RACT
under 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 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 approved into Pennsylvania's SIP and continue to be
implemented.\1\ On September 26, 2017, PADEP submitted a supplemental
SIP revision, dated September 22, 2017, which committed to address
various deficiencies identified by EPA in their May 16, 2016
``presumptive'' RACT II rule SIP revision.
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\1\ The RACT I Rule was approved by EPA into the Pennsylvania
SIP on March 23, 1998. 63 FR 13789. Through the current rule,
certain source-specific RACT I requirements will be superseded by
more stringent RACT II requirements. See Section II of this
preamble.
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On May 9, 2019, EPA conditionally approved the RACT II rule based
on the commitments PADEP made in its September 22, 2017 supplemental
SIP revision. See 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 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, specifically May 9, 2020. The SIP revisions
addressed in this rule are part of PADEP's efforts to meet the
conditions of its supplemental SIP revision and EPA's conditional
approval of the RACT II Rule.
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 case-by-case
RACT requirements for major sources in Pennsylvania subject to 25 Pa.
Code
[[Page 66258]]
129.99. In the Pennsylvania RACT SIP revisions, PADEP included a case-
by-case RACT determination for the existing emissions units at each of
these major sources of NOX and/or VOC that required a
source-specific RACT determination. In PADEP's RACT determinations, an
evaluation was completed to determine if previously SIP-approved, case-
by-case RACT emission limits or operational controls (herein referred
to as RACT I and contained in RACT I permits) were more stringent than
the new RACT II presumptive or case-by-case requirements. If more
stringent, the RACT I requirements will continue to apply to the
applicable source. If the new case-by-case RACT II requirements are
more stringent than the RACT I requirements, then the RACT II
requirements will supersede the prior RACT I requirements.\2\
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\2\ While the prior SIP-approved RACT I permit will remain part
of the SIP, this RACT II rule will incorporate by reference the RACT
II requirements through the RACT II permit and clarify the ongoing
applicability of specific conditions in the RACT I permit.
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Here, EPA is taking action on SIP revisions pertaining to case-by-
case RACT requirements for four major sources of NOX and/or
VOC in Pennsylvania, as summarized in Table 1.
Table 1--Four Major NOX and/or VOC Sources in Pennsylvania Subject to Case-by-Case RACT II Determinations Under
the 1997 and 2008 8-Hour Ozone NAAQS
----------------------------------------------------------------------------------------------------------------
Major source
Major source (county) 1-Hour ozone RACT source? pollutant (NOX and/or RACT II permit
(RACT I) VOC) (effective date)
----------------------------------------------------------------------------------------------------------------
Transco--Salladasburg Station 520 Yes....................... NOX and VOC........... 41-00001 (06/06/17).
(Lycoming).
Novipax (Berks)..................... Yes....................... VOC................... 06-05036 (12/19/2017).
Sunoco Partners Marketing & Yes....................... NOX and VOC........... 23-00119 (01/20/17).
Terminals (Delaware).
Global Advanced Metals USA, Inc. Yes....................... VOC................... 46-00037 (03/10/17).
(Montgomery).
----------------------------------------------------------------------------------------------------------------
The case-by-case RACT determinations submitted by PADEP consist of
an evaluation of all reasonably available controls at the time of
evaluation for each affected emissions unit, resulting in a PADEP
determination of what specific emission limit or control measures, if
any, satisfy RACT for that particular unit. The adoption of new,
additional, or revised emission limits or control measures to existing
SIP-approved RACT I requirements were specified as requirements in new
or revised Federally enforceable permits (hereafter RACT II permits)
issued by PADEP to the source. The RACT II permits, which revise or
adopt additional source-specific limits and/or controls, have been
submitted as part of the Pennsylvania RACT SIP revisions for EPA's
approval in the Pennsylvania SIP under 40 CFR 52.2020(d)(1). The RACT
II permits submitted by PADEP are listed in the last column of Table 1
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-2020-0189.\3\ EPA is
incorporating by reference in the Pennsylvania SIP, via the RACT II
permits, source-specific RACT emission limits and control measures
under the 1997 and 2008 8-hour ozone NAAQS for certain major sources of
NOX and VOC emissions.
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\3\ The RACT II permits are redacted versions of a facility's
Federally enforceable permits and reflect the specific RACT
requirements being approved into the Pennsylvania SIP.
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B. EPA's Proposed Action
PADEP's SIP revisions incorporate its determinations of source-
specific RACT II controls for individual emission units at major
sources of NOX and/or VOC in Pennsylvania, where those units
are not covered by or cannot meet Pennsylvania's presumptive RACT
regulation. After thorough review and evaluation of the information
provided by PADEP in its five SIP revision submittals for four major
sources of NOX and/or VOC in Pennsylvania, EPA proposed to
find that PADEP's case-by-case RACT determinations and conclusions
establish limits and/or controls on individual sources that are
reasonable and appropriately considered technically and economically
feasible controls.
PADEP, in its RACT II determinations, considered the prior source-
specific RACT I requirements and, where more stringent, retained those
RACT I requirements as part of its new RACT determinations. In the
NPRM, EPA proposed to find that all the proposed revisions to
previously SIP approved RACT I requirements would result in equivalent
or additional reductions of NOX and/or VOC emissions. The
proposed revisions should not interfere with any applicable requirement
concerning attainment or reasonable further progress with the NAAQS or
interfere with other applicable CAA requirements in section 110(l) of
the CAA.
Other specific requirements of Pennsylvania's 1997 and 2008 8-hour
ozone NAAQS case-by-case RACT determinations and the rationale for
EPA's proposed action were explained in the NPRM and its associated
technical support document (TSD) and will not be restated here.
III. Public Comments and EPA Responses
EPA received comments from seven commenters on the May 5, 2020
NPRM. 85 FR 26647. A summary of the comments and EPA's response are
discussed in this section of the preamble. A copy of the comments can
be found in the docket for this rule.
Comment 1: The commenter states that water/steam injection is a
control option for Transco Station 520's simple cycle turbines that was
inappropriately determined to be technically infeasible and indicates
that this control option is found on EPA's RACT/BACT/LAER Clearinghouse
(RBLC) as technically feasible in at least 10 natural gas fired simple
cycle turbines over the last 20 years. The commenter further states
that EPA had made a similar comment for the public record on the
technical feasibility of water/steam injection and had arbitrarily
reversed its position in the NPRM. The commenter claims that the
reasons given for technical infeasibility such as water/steam supply,
storage tanks, the source of water, and water treatment and
pretreatment are economic, and not technical, feasibility issues. For
these reasons, the commenter states that EPA should disapprove PADEP's
RACT
[[Page 66259]]
determination for Transco Station 520 and reevaluate the economic
feasibility of water/steam injection.
Response 1: The commenter is correct in stating that EPA made prior
comments suggesting that water/steam injection was a technically
feasible control option for natural gas fired simple cycle turbines in
gas transmission service that should be evaluated for economic
feasibility. However, EPA disagrees that it has arbitrarily changed its
position in proposing to approve the case-by-case RACT requirements for
the two Transco Station 520 simple cycle turbines. Both the facility
and PADEP responded to EPA's comment explaining why the water/steam
injection control option was not technically feasible at this specific
site.
PADEP conducted its case-by-case RACT analysis of potential
controls for Transco's natural gas fired simple cycle turbines pursuant
to the requirements of Pennsylvania's RACT regulations. The case-by-
case RACT II analysis requirements are set forth in 25 PA Code
129.99(c), which then references the RACT proposal requirements
identified in 25 Pa Code 129.92. As identified in Section 129.92(b)(1),
``[a]vailable control options are air pollution control technologies
with a reasonable potential for application at the source.'' Section
129.29(b)(2) further identifies that ``[a] determination of technical
infeasibility shall identify technical difficulties which would
preclude the successful use of the control option on the source.''
The water/steam injection control option requires a large volume of
purified water. The Transco facility is located in a remote location
without a viable on-site source of clean water. In order to have the
needed purified water on-site for water/steam injection, Transco would
need to drill an on-site well or transport water to an on-site water
purification facility. A water study would be needed to determine
whether and how an on-site well could be drilled. Transporting water to
the site would require the installation of a water purification
facility and large on-site storage tanks. The need to transport water
to the site for the use of water/steam injection also introduces
unreliability and the risk of insufficient water due to the
unpredictable nature of weather and transportation. The uncertainties
created by the need to transport water to the site increases the risk
of system failure because the Transco turbines are peaking units. Given
the nature of peak demand, these turbines are required to operate
immediately when necessary with little advanced notice.\4\
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\4\ See email dated May 18, 2017 from Williams to PADEP and
PADEP memorandum dated May 22, 2017, which are both part of the
record for this docket.
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For these reasons, the RACT analysis determined that water/steam
injection was technically infeasible for the Transco turbines. Lacking
an on-site water source or a reliable off-site source of on-demand
water, it was reasonable for PADEP to conclude that water/steam
injection was not an available control option with a ``reasonable
potential application at the source.'' While the need to install a
water purification system and large on-site storage tanks may be
factors that can be evaluated through an economic feasibility analysis,
the lack of an on-site water source and the risks and uncertainties of
an insufficient water supply due to the potential need for the on-
demand trucking of water are issues far more fundamental to determining
initially whether using water/steam injection is truly an available
control technology for these sources at this site. These circumstances
present ``technical difficulties which would preclude the successful
use of the control option on the affected source.'' After reviewing the
responses from the company and PADEP, EPA concluded that PADEP's RACT
determination that water/steam injection is not technically feasible
for the Transco Station 520 peaking turbines was a reasonable
conclusion based on Pennsylvania's RACT requirements.
Comment 2: The commenter complains that the Transco Station 520
redacted permit consists of non-uniform pages, where one added page is
in color and the remaining pages are in black and white. The commenter
claims that EPA illegally altered the state's submittal to correct a
mistake made by the state. The commenter refers to a prior proposed
rulemaking, EPA-R03-OAR-2017-0290, where the redacted permit for
Transco station 520, included in the docket for that proposed
rulemaking, did not include the 79.3 lbs/hr and 95.6 tpy RACT emission
limits. However, the commenter notes that the redacted permit in the
current docket does contain such RACT limits. The commenter states that
EPA must remit the SIP back to Pennsylvania to incorporate enforceable
RACT limitations.
Response 2: The commenter's concern relates to the RACT emission
limits for Source ID 106 in the Transco Station 520 Permit No. 41-
00001, Section D, I., Condition #004. The commenter notes that, in a
proposed rule from 2017, EPA-R03-OAR-2017-0290 which was never
finalized, this permit condition was not included in the redacted
permit to be incorporated into the SIP.\5\ This was an inadvertent
error because the emission limits contained in the permit condition
were always intended to be part of Pennsylvania's RACT determination
for this source. See, for example, the PADEP technical review memo,
dated February 22, 2017, the EPA TSD, and the full Transco Station 520
Permit No. 41-00001, all of which were in the docket for the 2017
proposed action. EPA, subsequently notified PADEP that the SIP
submittal for Transco Station 520 contained an incorrectly redacted
permit. On April 6, 2020, PADEP supplemented their SIP submittal with
the correctly redacted permit.\6\ The docket for the proposal for the
current rulemaking included a correctly redacted permit, which included
the 79.3 lbs/hr and 95.6 tpy RACT emission limits.\7\
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\5\ EPA never took any final action under the EPA-R03-OAR-2017-
0290 proposed rulemaking because of CBI issues with the docket. See
discussion in Supplementary Information section of this preamble.
\6\ PADEP supplemented its SIP revision submittal with a
corrected version of the redacted permits for Transco via email on
April 6, 2020. The revised redacted permit was appropriately added
to the supporting materials for the current proposed rulemaking. The
email from PADEP to EPA Region 3, dated April 6, 2020, is now being
added to the final docket along with the Final Rule Notice.
\7\ EPA notes that PADEP, in its RACT SIP revisions for Transco
Station 520, Novipax, SPTM, and Global Advanced Metals, included
some form of annual limits in the RACT II permits for those
facilities. EPA wishes to clarify that it is not approving any such
annual limits as RACT limits. Rather, because PADEP analyzed what
should be RACT under operating conditions that included annual
limits from the existing facility permit, and PADEP included those
requirements in its SIP submittal to us, EPA is incorporating those
annual limits into the SIP not as RACT control limits but for the
purpose of SIP strengthening.
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Comment 3: The commenter agrees with EPA's proposed approval of
PADEP's determination to avoid the use of the blowing agent 152a when
considering RACT alternatives to the use of pentane. The commenter
explains that coal is not the only substance that is bad for the
environment and claims that blowing agent 152a is an extremely
dangerous compound that is harmful to the environment because it is a
potent greenhouse gas, a carcinogen and produces carbon dioxide.
Response 3: While the commenter does not identify a specific
facility, we believe the commenter's comment applies to the Novipax
facility, where the blowing agent 152a was discussed in the RACT
analysis. EPA appreciates the support of the commenter for the Novipax
RACT determination.
[[Page 66260]]
Comment 4: The commenter states that EPA should require more
controls for Sunoco Partners Marketing and Terminals (SPMT), including
controls that exceed Pennsylvania's cost thresholds of $2,800/ton or
other states' $5,000/ton cost thresholds. The commenter claims that
facilities such as SPMT, which causes millions of dollars in
environmental damage and makes millions of dollars, can afford to do
more and should be required to do more. The commenter explains that the
area in which SPMT is located is historically poor, damaged by
industrial pollution, and is a neighborhood of black and brown people.
The commenter claims that EPA has a duty to consider environmental
justice and should disapprove the RACT determination for SPMT and
require PADEP to use a higher cost threshold and force RACT level
controls to be installed.
Response 4: There are seven emission units that required case-by-
case RACT determinations at the SPMT facility. The RACT determinations
are governed by the requirements of 25 Pa. Code 129.99, which requires
a technical and economic feasibility analysis of available control
options. Three of these emission units are the auxiliary boilers. The
SPMT auxiliary boilers are dual-fueled, burning both natural gas and
refinery gas. They are currently controlled with low NOX
burners and flue gas recirculation. PADEP's case-by-case RACT II
determination require these boilers to achieve a 0.05 lb
NOX/MMBtu emission limit, which will be incorporated into
the SIP through the current rule. This new limit tightens the prior
RACT I limit of 0.25 lb NOX/MMBtu emission limit. Although
there are no presumptive RACT requirements that apply to SPMT's dual-
fired boilers, the RACT II limit of 0.05 lb NOX/MMBtu is at
least twice as stringent as the presumptive RACT requirements at 25 Pa.
Code 129.97(g)(1) for combustion units equal to or greater than 50
MMBtu heat input. Because the SPMT boilers are already controlled and
achieve relatively low NOX emissions, additional controls
were found to be economically infeasible. The cost effectiveness
evaluation of the technically feasible control options for these
boilers determined a range of costs from $12,126 to $52,331/ton of
NOX reduced, a cost level well above the higher $5,000 cost
threshold identified by the commenter.\8\
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\8\ See Sunoco Partners Marketing and Terminals, L.P., RACT II
Proposal, Philadelphia, Pennsylvania, dated November 2016.
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The fourth emission unit subject to case-by-case RACT is the marine
vessel loading operation that is currently subject to the requirements
of 25 Pa. Code Sec. 129.81 and 40 CFR part 63, subpart Y, the National
Emission Standards for Marine Tank Vessel Loading Operations, which
contains additional requirements for vapor collection and leak
detection. All marine vessel loading at the facility is currently
controlled by a marine vapor recovery (MVR) system which captures gases
and directs them to the fuel gas system to be combusted as a fuel in
the auxiliary boilers. The RACT analysis of the marine vessel loading
operations concluded that there is no feasible control with a greater
control efficiency than the current MVR control technology. Because
there were no technically feasible controls better than the current
controls, a cost effectiveness analysis was not required.\9\
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\9\ Id.
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The fifth emission unit subject to case-by-case RACT is a single
cooling tower, which has a potential to emit 4.6 tpy VOC. There were no
technically or economically feasible control options for this source in
addition to what is already required under prior RACT SIP approvals,
which are equipment inspection and monitoring.\10\ The sixth and
seventh emission units subject to case-by-case RACT are fugitive leaks
from valves and fugitive leaks across the facility. Again, the RACT
analysis identified that there were no technically feasible controls
for these sources. For both of these sources, PADEP is requiring as
RACT compliance with 40 CFR part 60 subpart VV, Standards of
Performance for Equipment Leaks of VOC in the Synthetic Organic
Chemicals Manufacturing Industry (or VVa as appropriate), which
minimizes leaks from valves, flanges, and tanks through the use of
specified equipment, work practices and inspections.\11\
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\10\ Id.
\11\ Id.
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As identified in this preamble, PADEP followed the RACT analysis
requirements of 25 Pa. Code 129.99 and for only three sources was it
able to identify additional technically feasible control options. For
those sources, the three auxiliary boilers, the cost of added emission
reduction well exceeded even the higher cost effectiveness threshold
identified by the commenter. In its approval capacity, EPA shall
approve a state's proposed RACT proposal if it meets the statutory and
regulatory requirements of the program. CAA Section 110(k)(3). In this
case, EPA determined that PADEP's proposed RACT SIP was reasonable and
met the statutory and regulatory requirements.
The commenter also urges EPA to consider environmental justice as
part of the RACT determination for this facility. 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 determining RACT are those in the statue and
regulations, and environmental justice is not a statutory or regulatory
factor in the RACT analysis. As described in this preamble and in our
proposal document we believe it is appropriate to fully approve PADEP's
SIP submittal with respect to RACT for SPMT.
Comment 5: One commenter asserts that ``other neighboring states
such as New York and New Jersey both have cost effectiveness thresholds
set at or above $5,000 per ton, but here EPA arbitrarily allows a lower
dollar per ton threshold!'' The commenter goes on to question EPA's
approval of a lower cost threshold in Pennsylvania. Further, the
commenter states that ``EPA must retract their proposed approval and
set a uniform dollar per ton threshold based on, and consistent with,
past EPA actions'' and ``that the cost per ton threshold should at
least be consistent in the Ozone Transport Region (OTR).'' Lastly, the
commenter claims that ``EPA is arbitrary and capricious when approving
two different states RACT SIPs with inconsistent cost thresholds'' and
that ``EPA needs to set the bar, not let the states waffle in the wind
and never install controls.''
Response 5: EPA is aware that Pennsylvania considered cost-
effectiveness levels ($/ton removed) that are lower than other states,
such as New Jersey and New York as the commenter notes, when developing
the RACT II rule. However, EPA has not set a single cost, emission
reduction, or cost-effectiveness figure to fully define cost-
effectiveness in meeting the NOX or VOC RACT requirement.
Therefore, states have the discretion to determine what costs are
considered reasonable when establishing RACT for their sources. Each
state must make and defend its own determination on how to weigh these
values in establishing RACT.
As PADEP explained in its RACT II rulemaking, it did not establish
a bright-line cost effectiveness threshold in determining what is
economically reasonably for purposes of defining RACT.\12\ Instead, it
developed as guidance a cost-effectiveness threshold
[[Page 66261]]
of $2,800 per ton of NOX controlled and $5,500 per ton of
VOC controlled for RACT. Pennsylvania also determined that even
evaluating control technology options with an additional 25% margin, an
upper bound cost-effectiveness threshold of $3,500 per ton
NOX controlled and $7,000 per ton VOC controlled, would not
affect the add-on control technology decisions required by RACT. Id.
Pennsylvania determined that these higher cost-effectiveness thresholds
did not impact the determination of what add on control technology was
feasible. Pennsylvania also reviewed examples of benchmarks used by
other states: Wisconsin, $2,500 per ton NOX; Illinois,
$2,500-$3,000 per ton NOX; Maryland, $3,500-$5,000 per ton
NOX; Ohio, $5,000 per ton NOX; and New York,
$5,000-$5,500 per ton NOX.\13\
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\12\ 46 Pa. Bulletin 2036 (April 23, 2016).
\13\ PADEP Responses to Frequently Asked Questions, Final
Rulemaking RACT Requirements for Major Sources of NOX and
VOCs. October 20, 2016.
---------------------------------------------------------------------------
In a separate prior final agency action, EPA found that PADEP's
cost effectiveness thresholds are reasonable and reflect control levels
achieved by the application and consideration of available control
technologies, after considering both the economic and technological
circumstances of Pennsylvania's own sources. See 84 FR 20274, 20286
(May 9, 2019).
Comment 6: The commenter notes that good operating practices are
determined to be RACT for several sources at Global Advanced Metals.
However, the commenter claims that for Source IDs 102, 124, and 201,
those good operating practices are not defined in the permit.
Response 6: The commenter is correct, in part, in stating that good
operating practices have been determined as VOC RACT for Source IDs
102, 124, and 201. However, they are only one aspect of the overall
RACT II requirements imposed on the sources. For all three sources,
PADEP conducted a VOC RACT analysis per 25 Pa. Code 129.99, concluding
that the additional control technologies evaluated were either
technically and/or economically infeasible and that RACT would, among
other requirements, be operation and maintenance of the source in
accordance with manufacturers' specifications and good air pollution
control practices.\14\
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\14\ This identical permit condition can be found in Global
Advanced Metals' redacted Permit No. 46-00037, Section D, Source
102, VI. Condition #013; Source ID 124, VI. Condition #010; and
Source ID 201, I. Condition #002, which is part of the record of
this docket and will be incorporated into the SIP through this
action.
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As noted previously, PADEP imposed additional RACT requirements on
these sources based on existing permit conditions, which were
considered in the RACT analysis. For instance, Global Advanced Metals
currently utilizes a recovery unit to control methyl isobutyl ketone
(MIBK) emissions from Source ID 124, the extraction process in Building
74, and PADEP has imposed the requirement to operate this recovery unit
as a RACT requirement. The RACT II permit also includes efficiency
restrictions on the control device and extensive recordkeeping
requirements on operational factors such as flow rates, pressure drops,
MIBK content in influent and effluent, and maintenance downtime.\15\
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\15\ See Global Advanced Metals' redacted Permit No. 46-00037,
Section D, Source ID 124, I. Condition #003 and IV. Conditions #006,
#007 and #010; which is part of the record of this docket and will
be incorporated into the SIP through this action.
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The MIBK recovery system also helps to limit emissions from Source
ID 102, the tantalum salts process in Building 19.\16\ While the RACT
II permit does not specifically include the operation of the MIBK
recovery unit for Source 102, the recovery unit's operation is required
in the RACT II permit under Source 124, as identified in this preamble.
PADEP also imposed on Source 102 a throughput restriction on the number
of batches.\17\ Additionally, the RACT II for Source ID 201, the
wastewater treatment plant, included a requirement to provide PADEP
with relevant records found in the facility's National Pollutant
Discharge Elimination System (NPDES) permit, upon request.\18\
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\16\ See Global Advanced Metals' Alternative RACT Compliance
proposal, dated October 2016, which is part of the record for this
docket.
\17\ See Global Advanced Metals' redacted Permit No. 46-00037,
Section D, Source 102, I. Conditions #004, which is part of the
record for this docket and will be incorporated into the SIP through
this action.
\18\ See Global Advanced Metals' redacted Permit No. 46-00037,
Section D, Source ID 201, I. Condition #001, which is part of the
record for this docket and will be incorporated into the SIP through
this action.
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EPA concluded that ``good operating practices,'' which was
determined as VOC RACT for these three sources by PADEP, is adequately
defined in the facility's permit as ``operating and maintaining the
source in accordance with manufacturers' specifications.'' The
requirement to operate the source in accordance with the manufacturer's
specifications holds the facility accountable for operating and
maintaining each of these three sources per the guidance established by
the manufacturer specifically for that particular source. The good
operating practices requirement is further clarified and strengthened
by the additional RACT requirements for recovery unit operation,
operational restrictions, and recordkeeping included in the redacted
permit to be incorporated into the SIP.
Comment 7: The commenter notes that EPA is approving particulate
matter (PM) limits for Global Advanced Metals as part of the facility's
RACT determination. The commenter asks why and what relationship these
PM limits have in setting NOX and/or VOC RACT emission
limits for the source.
Response 7: While the commenter does not provide a specific
reference to the PM limits in question, EPA assumes the commenter is
referring to the PM limit of ``not to exceed 0.02 grains per dry
standard cubic foot'' as a control device efficiency restriction for
the RotoClone wet dust collector.\19\ The RotoClone wet dust collector
was not one of the control technologies examined by PADEP for the
control of VOCs from Source 109. Rather, it is a control technology for
PM. The PM limits were established under other regulatory programs and
not the RACT program. It was identified as an ongoing facility
requirement while reviewing the VOC RACT requirements for the fugitive
emissions from ethanol transfer and storage operations. The commenter's
concern about PM is warranted. The PM limits are not included in the
source's permit to address RACT requirements and therefore should not
be incorporated into the SIP through the current rule. PADEP has
subsequently submitted a revised redacted permit that does not include
the PM requirements for incorporation into the SIP.\20\
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\19\ Global Advanced Metals' redacted Permit No. 46-00037,
Section D., Source ID 109, Condition #003(b)(2).
\20\ See August 21, 2020 email from PADEP to EPA identifying
changes to redacted RACT II permit for Global Advanced Metals and
attaching the revised redacted permit. Both documents have been
added to the docket in this matter and the revised redacted permit
will be incorporated into the SIP. At the same time, PADEP has also
revised the original RACT II permit by deleting requirements for
Source 102 related to hydrogen flouride and hydrogen chloride for
similar reasons. Those facility requirements were not related to VOC
control.
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Comment 8: The commenter notes that for Source ID 201 at Global
Advanced Metals, the RACT determination includes the submission of
records required under the facility's NPDES permit. The commenter
claims that neither EPA nor PADEP provide justification or explanation
as to why submission of these records is necessary. The commenter
claims that EPA has no authority under the CAA to require submission of
records under the Clean Water Act (CWA), stating that the
[[Page 66262]]
Information Collection Request (ICR) approved for these records makes
no mention of allowing them to be used for purposes outside of the
NPDES program. The commenter claims that in order for EPA to require
submission of these records for CAA purposes, EPA would have to go
through the ICR process and calculate the burden on these sources to do
so.
Response 8: The commenter is correct that among the RACT
requirements for Source ID 201, the wastewater treatment plant (WWTP),
Condition #001 requires the facility to ``provide to the DEP, upon
request, copies of records required by the NPDES permit.'' \21\ This
condition is determined to be part of the source's VOC RACT
determination per 25 Pa. Code 129.100(d).
---------------------------------------------------------------------------
\21\ Global Advanced Metals' redacted Permit No. 46-00037,
Section D, Source ID 201, Condition #001.
---------------------------------------------------------------------------
EPA disagrees with the commenter that there is insufficient
justification or explanation as to why these records are relevant to
the VOC RACT determination for the WWTP. In its VOC RACT analysis,
PADEP explained that the constituents of the wastewater at Global
Advanced Metals include dissolved VOCs, which may be emitted to some
extent to the atmosphere in the treatment process.\22\ Knowledge of the
wastewater constituents informs PADEP's knowledge as to the
effectiveness of the wastewater treatment process in removing VOC
emissions at this source. Information on such constituents is contained
in the regular testing of total suspended solids and total dissolved
solids performed by Global Advanced Metals pursuant to its NPDES
permit. Therefore, this information is directly related to the control
of VOC air emissions from the WWTP.
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\22\ See PADEP's technical review memo, dated March 6, 2017,
which is included as part of the docket for this action.
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EPA also disagrees with the commenter's contentions about the use
of NPDES records for RACT purposes and believes the commenter may have
misinterpreted the nature of EPA's proposed action. In this SIP action,
EPA is not relying on any CWA information collection authorization and
is not adding such into the SIP. Rather, it is approving a legitimate
permit term established by PADEP, under its own independent authority
(the Air Pollution Control Act) to collect air emissions data, into the
Pennsylvania SIP. Data that is collected under the NPDES program
related to dissolved VOC constituents in a facility's wastewater is
such data and referring to the NPDES permit merely helps the facility
identify the required data but is not the authority being used to
collect it. The reference to the NPDES permit helps to identify that
the information needed to be supplied for compliance with the
Pennsylvania air permit is the same as the information being collected
under the CWA. It is merely a convenient way of identifying the data
needed to be reported under the air permit and is not the basis for the
state's authority to include it in the permit.
IV. Final Action
EPA is approving case-by-case RACT determinations for four sources
in Pennsylvania, as required to meet obligations pursuant to the 1997
and 2008 8-hour ozone NAAQS, as revisions to the Pennsylvania SIP.
V. Incorporation by Reference
In this document, EPA is finalizing regulatory text that includes
incorporation by reference. In accordance with requirements of 1 CFR
51.5, EPA is finalizing the incorporation by reference of source-
specific RACT determinations under the 1997 and 2008 8-hour ozone NAAQS
for certain major sources of VOC and NOX in Pennsylvania.
EPA has made, and will continue to make, these materials generally
available through https://www.regulations.gov and at the EPA Region III
Office (please contact the person identified in the For Further
Information Contact section of this preamble for more information).
Therefore, these materials have been approved by EPA for inclusion in
the SIP, have been incorporated by reference by EPA into that plan, are
fully Federally enforceable under sections 110 and 113 of the CAA as of
the effective date of the final rule of EPA's approval, and will be
incorporated by reference in the next update to the SIP
compilation.\23\
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\23\ 62 FR 27968 (May 22, 1997).
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VI. Statutory and Executive Order Reviews
A. General Requirements
Under the CAA, the Administrator is required to approve a SIP
submission that complies with the provisions of the CAA and applicable
Federal regulations. 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in
reviewing SIP submissions, EPA's role is to approve state choices,
provided that they meet the criteria of the CAA. Accordingly, this
action merely approves state law as meeting Federal requirements and
does not impose additional requirements beyond those imposed by state
law. For that reason, this action:
Is not a ``significant regulatory action'' subject to
review by the Office of Management and Budget under Executive Orders
12866 (58 FR 51735, October 4, 1993) and 13563 (76 FR 3821, January 21,
2011);
Is not an Executive Order 13771 (82 FR 9339, February 2,
2017) regulatory action because it is not a significant regulatory
action under Executive Order 12866.
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
[[Page 66263]]
Congress and to the Comptroller General of the United States. Section
804, however, exempts from section 801 the following types of rules:
Rules of particular applicability; rules relating to agency management
or personnel; and rules of agency organization, procedure, or practice
that do not substantially affect the rights or obligations of non-
agency parties. 5 U.S.C. 804(3). Because this is a rule of particular
applicability, EPA is not required to submit a rule report regarding
this action under section 801.
C. Petitions for Judicial Review
Under section 307(b)(1) of the CAA, petitions for judicial review
of this action must be filed in the United States Court of Appeals for
the appropriate circuit by December 18, 2020. 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 four case-by-case facilities for the 1997 and
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: September 22, 2020.
Cosmo Servidio,
Regional Administrator, Region III.
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 ``W.R. Grace and Co.--FORMPAC Div''; `` W. R.
Grace and Co.--Reading Plant''; ``Cabot Performance Materials--
Boyertown''; ``Sunoco, Inc. (R&M); Marcus Hook Plant''; and
``Transcontinental Gas Pipeline Corporation'' (Permit No. PA-41-0005A);
and
0
b. Adding the following entries at the end of the table: ``Transco--
Salladasburg Station 520 (formerly referenced as Transcontinental Gas
Pipeline Corporation)''; ``Novipax (formerly referenced as W. R. Grace
and Co.--FORMPAC Div and W. R. Grace and Co.--Reading Plant)'';
``Sunoco Partners Marketing & Terminals (formerly referenced as Sunoco,
Inc. (R&M); Marcus Hook Plant)''; and ``Global Advanced Metals USA,
Inc. (formerly referenced as Cabot Performance Materials--Boyertown)''.
The revisions and additions read as follows:
Sec. 52.2020 Identification of plan.
* * * * *
(d) * * *
(1) * * *
--------------------------------------------------------------------------------------------------------------------------------------------------------
Additional
explanations/ Sec.
Name of source Permit No. County State effective date EPA approval date Sec. 52.2063 and
52.2064 citations
\1\
--------------------------------------------------------------------------------------------------------------------------------------------------------
* * * * * * *
W. R. Grace and Co.--FORMPAC Div. PA-06-1036............. Berks.................. 5/12/95................ 5/16/96, 61 FR 24706 See also
52.2064(b)(2).
W. R. Grace and Co.--Reading PA-06-315-001.......... Berks.................. 6/4/92................. 5/16/96, 61 FR 24707 See also
Plant. 52.2064(b)(2).
* * * * * * *
Cabot Performance Materials-- OP-46-0037............. Montgomery............. 4/13/99................ 12/15/00, 65 FR See also
Boyertown. 78418. 52.2064(b)(4).
* * * * * * *
Sunoco, Inc. (R&M); Marcus Hook CP-23-0001............. Delaware............... 6/8/95, 8/2/01......... 10/30/01, 66 FR See also
Plant. 54699. 52.2064(b)(3).
* * * * * * *
Transcontinental Gas Pipeline PA-41-0005A............ Lycoming............... 8/9/95................. 8/24/05, 70 FR 49496 See also
Corporation. 52.2064(b)(1).
* * * * * * *
Transco--Salladasburg Station 520 41-00001............... Lycoming............... 6/6/17................. October 19, 2020, 52.2064(b)(1).
(formerly referenced as [INSERT FEDERAL
Transcontinental Gas Pipeline REGISTER CITATION].
Corporation).
Novipax (formerly referenced as 06-05036............... Berks.................. 12/19/17............... October 19, 2020, 52.2064(b)(2).
W. R. Grace and Co.--FORMPAC Div [INSERT FEDERAL
and W. R. Grace and Co.--Reading REGISTER CITATION].
Plant).
Sunoco Partners Marketing & 23-00119............... Delaware............... 1/20/17................ October 19, 2020, 52.2064(b)(3).
Terminals (formerly referenced [INSERT FEDERAL
as Sunoco, Inc. (R&M); Marcus REGISTER CITATION].
Hook Plant).
[[Page 66264]]
Global Advanced Metals USA, Inc. 46-00037............... Montgomery............. 3/10/17................ October 19, 2020, 52.2064(b)(4).
(formerly reference as Cabot [INSERT FEDERAL
Performance Materials-- REGISTER CITATION].
Boyertown).
--------------------------------------------------------------------------------------------------------------------------------------------------------
\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 (b) 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).
* * * * *
(b) Approval of source-specific RACT requirements for 1997 and 2008
8-hour ozone national ambient air quality standards for the facilities
listed below are incorporated as specified below. (Rulemaking Docket
No. EPA-OAR-2020-0189).
(1) Transco--Salladasburg Station 520--Incorporating by reference
Permit No. 41-00001, issued June 6, 2017, as redacted by Pennsylvania,
which supersedes the prior RACT Permit No. 41-0005A, issued August 9,
1995, except for Conditions 3, 4, 6, 8, 14, and 18, which remain as
RACT requirements applicable to the three 2050 hp Ingersoll Rand
engines #1, 2, and 3 (Source IDs P101, P102, P103). See also Sec.
52.2063(d)(1)(i) for prior RACT approval.
(2) Novipax--Incorporating by reference Permit No. 06-05036, issued
December 19, 2017, as redacted by Pennsylvania, which supersedes the
prior RACT Plan Approval No. 06-1036, issued May 12, 1995 to W. R.
Grace and Co. FORMPAC Division, except for Conditions 3, 4 (applicable
to two pentane storage tanks, Source IDs 101 and 101A), 5 (applicable
to extruders, Source ID 102, and facility wide to Source IDs 103, 104,
105, 106, 106B, 106C, 107, and 108), 7 (applicable to Source IDs 101,
101A, and 102) and 8 (applicable to Source IDs 101, 101A, and 102),
which remain as RACT requirements applicable to the indicated sources,
and Plan Approval No. 06-315-001, issued June 4, 1992 to W. R. Grace
and Co.--Reading Plant, except for Conditions 4 (applicable to Source
ID 102), 5 (applicable to Source IDs 101 and 101A), and 6 (applicable
to Source IDs 101, 101A, and 102), which remain as RACT requirements
applicable to the indicated sources. See also Sec.
52.2063(c)(108)(i)(B)(6) for prior RACT approvals.
(3) Sunoco Partners Marketing & Terminals--Incorporating by
reference Permit No. 23-00119, issued January 20, 2017, as redacted by
Pennsylvania, which supersedes the prior RACT Compliance Permit No. CP-
23-0001, issued June 8, 1995 and amended on August 2, 2001, except for
Conditions 5E (applicable to diesel engine and stormwater pumps, Source
ID 113), 6A (applicable to marine vessel loading, Source ID 115), 6B
(tank truck loading), 6C (applicable to cooling tower 15-2B, Source ID
139), and 6D (applicable to waste water treatment, Source 701), which
remain as RACT requirements applicable to the indicated sources. See
also Sec. 52.2063(c)(179)(i)(B)(6) for prior RACT approval.
(4) Global Advanced Metals USA, Inc.--Incorporating by reference
Permit No. 46-00037, issued March 10, 2017, as redacted by
Pennsylvania, which supersedes the prior RACT Permit No. OP-46-0037,
issued April 13, 1999, except for condition 15, which remains as a RACT
requirement applicable to the tantalum salts process (Source ID 102),
the extraction process (Source ID 124), the wastewater treatment plant
(Source ID 201), and fugitive emissions from ethanol transfer and
storage (Source 109). See also Sec. 52.2063(c)(143)(i)(B)(20) for
prior RACT approval.
[FR Doc. 2020-21438 Filed 10-16-20; 8:45 am]
BILLING CODE 6560-50-P