Approval and Promulgation of Air Quality Implementation Plans; Pennsylvania; Regional Haze State Implementation Plan, 41279-41284 [2012-16428]
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the CAA. Accordingly, this action
merely proposes to approve 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 Order 12866 (58 FR 51735,
October 4, 1993);
• 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.
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, pertaining to Maryland’s
RACT provisions for NOX and VOCs
with respect to the 1997 8-hour ozone
may not be challenged later in
proceedings to enforce its requirements.
(See section 307(b)(2).)
B. Submission to Congress and the
Comptroller General
List of Subjects in 40 CFR Part 52
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing this action and other
required information to the U.S. Senate,
the U.S. House of Representatives, and
the Comptroller General of the United
States prior to publication of the rule in
the Federal Register. A major rule
cannot take effect until 60 days after it
is published in the Federal Register
This action is not a ‘‘major rule’’ as
defined by 5 U.S.C. 804(2).
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 September 11, 2012. Filing a
petition for reconsideration by the
Environmental protection, Air
pollution control, Incorporation by
reference, Nitrogen dioxide, Ozone,
Reporting and recordkeeping
requirements, Volatile organic
compounds.
Authority: 42 U.S.C. 7401 et seq.
Dated: June 27, 2012.
W.C. Early,
Acting Regional Administrator, Region III.
Therefore, 40 CFR part 52 is amended
as follows:
PART 52—[AMENDED]
1. The authority citation for 40 CFR
part 52 continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
2. In § 52.1070, the table in paragraph
(e) is amended by adding the entry for
‘‘RACT under the 1997 8-hour ozone
NAAQS’’ at the end of the table to read
as follows:
■
§ 52.1070
*
Identification of plan.
*
*
(e) * * *
*
*
Name of non-regulatory SIP revision
Applicable geographic area
State submittal
date
EPA approval date
*
*
RACT under the 1997 8-hour ozone
NAAQS.
*
*
Statewide ........................................
10/17/11
*
*
7/13/12 [Insert page number where
the document begins].
[FR Doc. 2012–16949 Filed 7–12–12; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
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[EPA–R03–OAR–2012–0002; FRL–9695–5]
Approval and Promulgation of Air
Quality Implementation Plans;
Pennsylvania; Regional Haze State
Implementation Plan
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
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Additional
explanation
*
EPA is finalizing the limited
approval of the Regional Haze State
Implementation Plan (SIP) (hereafter RH
SIP) revision submitted by the
Commonwealth of Pennsylvania
(Pennsylvania). EPA is taking this action
because Pennsylvania’s SIP revision, as
a whole, strengthens the Pennsylvania
SIP. This action is being taken in
accordance with the requirements of the
Clean Air Act (CAA) and EPA’s rules for
states to prevent and remedy future and
existing anthropogenic impairment of
visibility in mandatory Class I areas
SUMMARY:
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through a regional haze program. EPA is
also approving this revision as meeting
the infrastructure requirements relating
to visibility protection for the 1997 8hour ozone National Ambient Air
Quality Standard (NAAQS) and the
1997 and 2006 fine particulate matter
(PM2.5) NAAQS.
DATES: This final rule is effective on
August 13, 2012.
ADDRESSES: EPA has established a
docket for this action under Docket ID
Number EPA–R03–OAR–2012–0002. All
documents in the docket are listed in
the www.regulations.gov Web site.
Although listed in the electronic docket,
some information is not publicly
available, i.e., 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 either electronically through
www.regulations.gov or in hard copy for
public inspection during normal
business hours at the Air Protection
Division, U.S. Environmental Protection
Agency, Region III, 1650 Arch Street,
Philadelphia, Pennsylvania 19103.
Copies of the Commonwealth’s
submittal are available at the
Pennsylvania Department of
Environmental Protection, Bureau of Air
Quality Control, P.O. Box 8468, 400
Market Street, Harrisburg, Pennsylvania
17105.
FOR FURTHER INFORMATION CONTACT:
Melissa Linden, (215) 814–2096, or by
email at linden.melissa@epa.gov.
SUPPLEMENTARY INFORMATION:
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I. Background
Throughout this document, whenever
‘‘we,’’ ‘‘us,’’ or ‘‘our’’ is used, we mean
EPA. On January 26, 2012, EPA
published a notice of proposed
rulemaking (NPR) for Pennsylvania (77
FR 3984). The NPR proposed limited
approval of Pennsylvania’s RH SIP. The
formal SIP revision was submitted by
the Pennsylvania Department of
Environmental Protection (PADEP) on
December 20, 2010. This revision also
meets the requirements of CAA section
110(a)(2)(D)(i)(II) and (a)(2)(J), relating to
visibility protection for the 1997 8-hour
ozone NAAQS and the 1997 and 2006
PM2.5 NAAQS.
II. Summary of SIP Revision
The SIP revision includes a long term
strategy with enforceable measures
ensuring reasonable progress towards
meeting the reasonable progress goals
for the first planning period through
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2018. Pennsylvania’s RH SIP contains
the emission reductions needed to
achieve Pennsylvania’s share of
emission reductions for the Class I areas
they impact. The specific requirements
of the CAA and EPA’s Regional Haze
Rule (64 FR 35714, July 1, 1999) and the
rationale for EPA’s proposed action are
explained in the NPR and are not
restated here. EPA received several
adverse comments and one letter of
support on the January 26, 2012 NPR.
One of those adverse comments
requested a change to PADEP’s best
available retrofit technology (BART)
determination for GenOn Energy’s
Cheswick Generating Station.
Pennsylvania can revise this
determination in a future SIP revision to
address comments raised by GenOn
Energy. A summary of the comments
submitted and EPA’s responses are
provided in section III of this document.
III. Summary of Public Comments and
EPA Responses
Comment: EPA proposed approval of
Pennsylvania’s RH SIP on January 26,
2012 with a docket that includes most
of the RH SIP submission from PADEP
except Appendix Z, which is the
comment and response document.
Response: PADEP did not submit an
Appendix Z, nor was it referenced in
the rulemaking. The PADEP comment
and response document is Appendix
AA and can be found in the EPA docket
for this action, docket No. EPA–R03–
OAR–2012–0002.
Comment: The commenter stated that
Pennsylvania has 15 BART-eligible
electric generating units (EGUs) that
include 28 individual units that are
among the largest uncontrolled sources
for nitrogen oxides (NOX) and sulfur
dioxide (SO2). The commenter claimed
PADEP did not conduct any five-step
determinations for BART at these EGUs
for NOX and SO2. It relied upon the
pending ‘‘cross state air pollution rule
(CSAPR) Better than BART’’
determination.
Response: In today’s action, EPA is
finalizing a limited approval of
Pennsylvania’s RH SIP based on its
reliance on the Clean Air Interstate Rule
(CAIR). EPA did not propose to find that
participation in the Transport Rule1 is
an alternative to BART in this action.
EPA addressed these comments
concerning the Transport Rule as a
BART alternative in a final action that
was published on June 7, 2012 (77 FR
1 The Transport Rule is also known as the Cross
State Air Pollution Rule (CSAPR) and was proposed
by EPA to help states reduce air pollution and
attain CAA standards. See 75 FR 45210 (August 2,
2010) (proposal) and 76 FR 48208 (August 8, 2011)
(final rule).
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33642). EPA’s response to these
comments can be found in Docket ID
No. EPA–HQ–OAR–2011–0729 at
www.regulations.gov.
Comment: The commenter stated that
BART determinations must consider
filterable PM10, PM2.5 and condensable
PM. The commenter stated that the
PADEP BART determinations are
expressed in total PM, but the cost
analyses were conducted based on
filterable PM10. The commenter
requested EPA to disapprove PADEP’s
determinations and adopt a FIP that
establishes BART limits for filterable
PM10, PM2.5 and condensable PM
because PADEP set BART limits for
filterable PM10 and filterable PM.
Response: EPA disagrees with the
commenter that the PM BART limits
should be disapproved. The controls on
the facilities considered by PADEP for
the emission limits in the BART
determinations are effective in reducing
filterable and condensable particulates.
Separate emission limits for each are not
required for BART.
Comment: The commenter claimed
PADEP’s BART determinations and
EPA’s proposed approval of these
determinations are fundamentally
flawed, arbitrary, and unlawful. The
commenter stated that source-specific
process design information is required
to make BART determinations which
PADEP did not provide. One commenter
stated PADEP’s BART determinations
were fundamentally flawed for steps
one through four of the BART
determination process. The commenter
stated the flaw in step one was that
PADEP did not address all available
technologies for each BART
determination. The commenter stated
the flaw in step two was that PADEP did
not appropriately interpret technical
feasibility of control options in
accordance with the Guidelines for
BART Determinations under the
Regional Haze Rule at Appendix Y to 40
CFR part 51 (hereafter the BART Rule).
See 70 FR 39104 (July 6, 2005). The
commenter stated the flaw in step three
was that PADEP did not rank the control
effectiveness for all EGU and most nonEGU BART determinations. The
commenter stated the flaw in step four
was that PADEP eliminated
technologies based on non-air quality
environmental impacts that are common
throughout the industry.
Response: Congress crafted the CAA
to provide for states to take the lead in
developing implementation plans but
balanced that decision by requiring EPA
to review the plans to determine
whether a SIP meets the requirements of
the CAA. In undertaking such a review,
EPA does not usurp a state’s authority
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but ensures that such authority is
reasonably exercised. BART
determinations under the regional haze
program are the responsibility of the
states, which have the freedom to
determine the weight and significance
of the statutorily required five-factors in
a BART determination. EPA then
reviews a state’s determination as
included in its regional haze plan.
Pennsylvania performed the required
BART determinations for its BARTeligible sources. In Appendix J of its RH
SIP submittal, Pennsylvania considered
the required five-factors and explained
its conclusions for each specific source.
As identified in Appendix J,
Pennsylvania performed its BART
determinations evaluating the fivefactors required. Appendix J describes
the steps Pennsylvania took in
evaluating BART and provides a basis
for Pennsylvania’s BART
determinations based on those fivefactors. The modeling of source impacts
and technology reviews for specific
source categories can be found in
Pennsylvania’s Appendices I, P and Q
respectively, which support
Pennsylvania’s BART determinations
found in Appendix J. EPA determined
that PADEP did address all available
technologies and appropriately
determined technical feasibility of those
technologies. The ranking of control
technologies is not a requirement of step
three (evaluating the control
effectiveness) in BART determinations.
The evaluation of non-air quality
impacts as part of step four of the BART
determination should be made based on
a consideration of the specific
circumstances of that source, so the
same technology may have a different
degree of impact dependent on the
source. EPA determined that PADEP did
address step four for the BART
determinations in accordance with the
BART Rule.
Comment: The commenter stated that
the PM limit for EGUs is invalid for
BART. Pennsylvania used an outdated
0.1 pound per million British thermal
unit (lb/MMBtu) limit for filterable PM.
The proposed BART limit is much
higher than accepted as BART (or as
best available control technology known
as BACT), and much higher than levels
currently being achieved at many other
similar facilities.
Response: EPA disagrees that the PM
BART limits are invalid. While BACT is
similar to BART, BACT has a four factor
analysis of environmental impact,
energy consumption, economic impact,
and other costs. BART determinations
however involve a five factor analysis of
all technologies available for retrofit,
consideration of current control
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technologies, cost of compliance of
controls, remaining useful life of the
facility, energy and non air-quality
environmental impacts, and visibility
impacts. BART is not a required topdown evaluation like BACT. As stated
in the BART Rule, the states should
retain the discretion to evaluate control
options in whatever order they choose,
so long as the state explains its analysis
of the CAA factors. PADEP did address
each of the five factors in its BART
determination summaries in Appendix J
of the PADEP December 20, 2010 RH
SIP submittal. Because BART and BACT
involve different evaluations, EPA
believes it is reasonable to have
different outcomes and different limits
for each review. The specific BACT
limits cited by the commenter cannot
automatically be considered valid for
BART.
Comment: BART guidelines provide
that maximum available control
technology (MACT) for hazardous air
pollutants (HAPs) should be taken into
account for determining BART as stated
in 40 CFR part 51, appendix Y, Section
IV.C. The commenter stated that
Pennsylvania EGUs are subject to EPA’s
Mercury and Air Toxics Standards
(MATS Rule) which was published on
February 16, 2012 (77 FR 9304). The
commenter stated that EPA must take
these requirements into account in
approving any BART determination
because all statutory factors should be
included. The commenter stated that
PADEP’s BART determinations for PM
limits of 0.1 lb/MMBtu cannot be
approved because those limits are much
higher than the 0.03 lb/MMBtu limit in
the final MATS Rule as a surrogate limit
for non-mercury metal HAPs.
Response: EPA agrees that we do
require all statutory factors to be
included in the BART determinations
that are applicable at the time the
determinations are done. EPA cannot
require BART determinations to predict
future requirements and to include
those as BART. When EPA issues new
rules, the states must adopt them as
appropriate. The final MATS Rule was
promulgated after the proposed limited
approval of the PM BART
determinations in the Pennsylvania RH
SIP on January 26, 2012.
Comment: The commenter stated that
EPA claimed it included all BARTeligible sources in the CSAPR Betterthan-BART analysis, but the analysis
omitted the BART-eligible oil-fired
EGUs as identified by PADEP. These
facilities in Pennsylvania are Trigen/
Edison Station Units 3 and 4; Trigen/
Schuylkill Station Unit 26; Eddystone
Units 3 and 4; and Martins Creek Units
3 and 4. EPA’s CSAPR Better-than-
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BART analysis compared projected EGU
emissions at the presumptive EGU
BART limits to projected emissions
under CSAPR. EPA then modeled these
scenarios against the 2014 baseline that
excludes both BART and CSAPR. The
visibility benefits from this modeling
were then averaged across all Class I
areas. The commenter stated that EPA
claims this analysis shows that CSAPR
will result in more emissions reductions
than BART and cites to 76 FR 82225.
The commenter claimed that CSAPR
will not achieve greater reasonable
progress toward the national visibility
goal than source-specific BART for
EGUs in Pennsylvania. Even if CSAPR
could lawfully substitute for BART, the
commenter claimed the instant
rulemaking would have to include
separate NOX and SO2 BART
determinations for Pennsylvania EGUs
because CSAPR does not in fact perform
better than BART.
Response: These comments are
beyond the scope of this rulemaking.
EPA’s response to comments concerning
the ‘‘CSAPR is Better-than-BART’’
action can be found in Docket ID No.
EPA–HQ–OAR–2011–0729 at
www.regulations.gov.
Comment: The commenter stated that
PADEP evaluated step five of the BART
determinations in a piecemeal fashion,
considering the visibility impact to each
Class I area separately and determined
controls based on the most highly
impacted Class I area. PADEP’s
approach resulted in significantly
underestimating visibility
improvements compared to
implementing BART for PA sources.
Most of the BART-eligible sources are
clustered in the southwest corner of the
state, near four Class I areas. Most of the
remaining BART-eligible sources are
clustered in the southeast region of the
state, near Brigantine Class I area, with
Montour in the middle of the state. The
federal land managers (FLMs) made
similar comments on the draft
Pennsylvania RH SIP. PADEP
responded that the BART Rule does not
require a ‘‘cumulative’’ impact analysis
and stated that EPA has provided no
guidance on this issue. The commenter
disagreed and stated that the BART Rule
is clear that multiple sources and Class
I areas are to be considered. The
commenter cited to 70 FR 39161–62.
The commenter claimed EPA
recommended that Nebraska
Department of Environmental Quality
(NDEQ) consider calculating the
visibility improvement at multiple Class
I areas.
Response: EPA disagrees with this
comment in general. The BART Rule
pages referred to by the commenter
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address determining whether a facility
is BART-eligible and not the applicable
approach defined later in the guidelines
for BART-subject sources. EPA agrees
with PADEP that the BART Rule does
not require a ‘‘cumulative’’ impact
analysis as part of the BART
determination for a specific source. The
guidelines do give the option to evaluate
cumulative impacts to multiple Class I
areas which EPA does recommend but
does not require the state to do. As
noted by the language used by EPA to
NDEQ, we recommend consideration of
the cumulative approach.
Comment: The commenter stated that
the PADEP source-specific analyses in
Appendix J rejected every single control
option as not cost effective using one or
both of the following two measures:
dollar per ton or dollar per deciview.
However, no significance thresholds
were established for either. The FLMs
also commented on this issue during the
PADEP review process. PADEP’s
response to the FLMs was that it did not
establish or use ‘‘bright line thresholds
for cost or for visibility improvement in
making BART determinations’’ in
Appendix AA of the Pennsylvania RH
SIP submittal. The commenter noted
that based on determinations in other
states, the acceptable cost effectiveness
value ranges from $5,000 per ton to
$10,000 per ton. The commenter
claimed that many of PADEP’s ‘‘no
control’’ determinations fall well below
this range.
Response: EPA’s BART guidelines in
the BART Rule do not require
Pennsylvania to develop a specific
threshold, but rather to evaluate each
BART determination on a case-by-case
basis for each source. EPA has not
established a specific cost threshold that
makes a particular control option BART
based on just a dollars per ton number.
All five factors must be compared to
determine the level of control that is
BART on a case-by-case basis. As
discussed in the NPR, EPA finds the
BART determinations from PADEP
reasonable.
Comment: The commenter stated that
EPA unreasonably relies on CSAPR for
BART and that EPA failed to adequately
review Pennsylvania’s BART
determinations.
Response: For BART determinations
of sources other than EGUs, EPA
reviewed PADEP’s BART
determinations in the December 20,
2010 Pennsylvania RH SIP submittal
and approves the conclusions as the
determinations are reasonable.
Comments related to CSAPR as an
alternative to BART for EGUs are
beyond the scope of this rulemaking.
EPA addressed similar comments
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concerning the Transport Rule as a
BART alternative in a final action that
was signed on May 30, 2012 (77 FR
33642, June 7, 2012). The EPA’s
response to these comments can be
found in Docket ID No. EPA–HQ–OAR–
2011–0729 at www.regulations.gov.
Comment: The commenter stated that
EPA’s proposed SO2 reductions from
Pennsylvania sources as substitute
measures addressing Pennsylvania’s
failure to adopt the Mid-Atlantic/
Northeast Visibility Union (MANE–VU)
low sulfur fuel oil strategy are largely
reliant upon the Portland Generating
Station SO2 reductions from the
federally enforceable order from EPA
responding to the CAA section 126
petition from the State of New Jersey.
The commenter also states that this
order has been appealed in the federal
Court of Appeals and should not be
relied upon due to its uncertainty.
Response: EPA disagrees with the
commenter. The rule issued in response
to the CAA section 126 petition from the
State of New Jersey for the Portland
Generating Station is federally
enforceable and can be relied upon
because it has not been stayed, nor has
it been revoked at this time. The
reductions can be relied upon for
reasonable progress at this time because
it is a federally enforceable measure. If
these reductions do not occur, then
PADEP may have to address them in the
five year look back by submitting a SIP
revision.
Comment: The commenter stated that
Pennsylvania’s failure to adopt the lowsulfur fuel oil strategy that was included
in New Jersey’s reasonable progress
goals cannot be supplemented by SO2
emission reductions without modeling
the impacts as required by 40 CFR
51.308(d)(3)(iii).
Response: EPA disagrees with the
commenter. 40 CFR 51.308(d)(3)(iii)
provides that a state ‘‘must document
the technical basis, including modeling,
monitoring and emissions information,
on which the State is relying to
determine its apportionment of
emission reduction obligations
necessary for achieving reasonable
progress in each mandatory Class I
Federal area it affects. The State may
meet this requirement by relying on
technical analyses developed by the
RPO and approved by all State
participants. The State must identify the
baseline emissions inventory on which
its strategies are based.’’ 40 CFR
51.308(d)(3)(iii). EPA did identify the
baseline emissions for the measures
substituted to address the SO2
reductions that would have come from
Pennsylvania’s low-sulfur fuel oil
strategy, and the modeling impact of the
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MANE–VU rule was done by the
regional planning organization (RPO).
The low-sulfur fuel oil strategy was an
area source rule and the substituted
emission reductions are from specific
sources that are located closer to the
Brigantine Class I area. Thus, the
substitution of SO2 reductions does
meet the requirements in 40 CFR
51.308(d)(3)(iii).
Comment: The commenter stated that
both the EPA proposed action for
CSAPR Better-than-BART and EPA’s
proposed action on Pennsylvania’s RH
SIP stated that EPA was taking action on
long-term strategy in a separate notice.
The commenter stated that neither
rulemaking acted on the long-term
strategy for Pennsylvania which is
untenable according to the commenter.
Response: The commenter has made
an incorrect assumption. The EPA
stated in the proposed action for CSAPR
Better-than-BART that we proposed a
limited disapproval of the regional haze
SIPs that have been submitted by
several states including Pennsylvania
and that these states ‘‘fully consistent
with the EPA’s regulations at the time,
relied on CAIR requirements to satisfy
the BART requirement and the
requirement for a long-term strategy
sufficient to achieve the state-adopted
reasonable progress goals’’ (76 FR
82221). We further stated that ‘‘CAIR
and CAIR FIP requirements, however,
will only remain in force to address
emissions through the 2011 control
period and thus CAIR cannot be relied
upon in a SIP as a substitute for BART
or as part of a long-term control
strategy.’’ Id. EPA proposed and
finalized a limited disapproval for the
Pennsylvania RH SIP for the long-term
strategy due to reliance on CAIR. The
other long-term strategy measures are
covered under the limited approval
proposed for Pennsylvania’s RH SIP in
77 FR 3988. Therefore, all long-term
control strategies beyond reliance on
CAIR are included in the limited
approval previously proposed, and now
finalized, by this action. The final
limited disapproval and FIP was
published on June 7, 2012, addressing
the deficiencies of the long-term strategy
insofar as it relied on CAIR (77 FR
33642).
Comment: The commenter requested
a conditional approval of
Pennsylvania’s RH SIP requiring the
implementation of the lower-sulfur fuel
strategy since it was relied upon for
establishing the reasonable progress
goals for MANE–VU Class I areas.
Multiple commenters also stated that
EPA’s substitution of emission
reductions is not permitted under the
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Regional Haze Rule for reasonable
progress goals for visibility.
Response: EPA does not agree that a
conditional approval is appropriate for
the Pennsylvania RH SIP given our
determination that the plan meets the
relevant applicable requirements. As set
forth in a prior response, EPA disagrees
that substitution of emission reductions
is not permitted for reasonable progress
goals.
Comment: The commenter stated that
EPA should have disapproved
Pennsylvania’s RH SIP due to PADEP’s
failure to implement a proposed lowsulfur fuel oil strategy. The commenter
stated that EPA should have demanded
the additional 5,702 tons of SO2
emission reductions from Pennsylvania
instead of saying that EPA does not
anticipate the difference will interfere
with the ability of other states to achieve
reasonable progress goals.
Response: EPA disagrees with the
commenter. Disapproving the entire
Pennsylvania RH SIP would have
slowed implementation of other
controls listed in the RH SIP. As
explained in the NPR, we anticipate that
the Pennsylvania RH SIP will ensure
sufficient emission reductions to meet
its share needed for nearby states to
achieve their reasonable progress goals.
If it is determined that the shortfall of
SO2 emission reductions impedes the
achievement of reasonable progress,
then at the time of the five year periodic
review PADEP may need to submit a SIP
revision requiring those additional
reductions.
Comment: One commenter stated that
the PADEP BART determination for
GenOn Energy’s Cheswick Generating
Station included emission limits
including PM which were inconsistent
with the plant’s current permits. The
commenter requested EPA to require
PADEP to revise the BART
determination.
Response: EPA evaluated the BART
determination and agrees with PADEP’s
determination of the appropriate BART
limit based on current controls. In
setting the BART limits, PADEP appears
to have set emission limits for the
facility that are far more stringent than
intended. If Pennsylvania submits a
revised BART determination for the
Cheswick Generating Station, EPA
commits to act expeditiously on the
revised SIP submittal.
Comment: Two commenters stated
that PADEP did not address reasonable
progress requirements for addressing
MANE–VU’s modeled exceedance of the
uniform rate of progress (URP) at Dolly
Sods Class I area.
Response: Reasonable progress goals
are set by the Class I area state. West
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Virginia did not request any reductions
from Pennsylvania to meet the URP as
modeled by Visibility Improvement
State and Tribal Association of the
Southeast (VISTAS). The discrepancies
in modeling between the two RPOs were
addressed in Pennsylvania’s RH SIP
submittal. The requirement for the state
consultation process was met, and
Pennsylvania fulfilled what was
requested by West Virginia.
Comment: The commenter stated that
Pennsylvania’s modeling for the RH SIP
submittal did not address the significant
growth in emissions from Marcellus
Shale natural gas drilling operations and
therefore does not support reasonable
progress.
Response: EPA disagrees with the
commenter because reasonable progress
goals are set by the Class I area and are
evaluated during the 5 year periodic
review. In addition, CAA section
169A(g)(1) requires states to take into
consideration a number of factors for
reasonable progress. States have
flexibility in how to take into
consideration these statutory factors and
any other factors that are determined to
be relevant. As previously explained
herein and in the NPR, we anticipate
that the Pennsylvania RH SIP will
ensure sufficient emission reductions
for reasonable progress goals. During the
five year periodic review, any
significant changes in projected
emissions can be addressed.
IV. Final Action
EPA is finalizing its limited approval
of the revision to the Pennsylvania SIP
submitted on December 20, 2010 that
addresses regional haze for the first
implementation period in Pennsylvania.
EPA is issuing a limited approval of the
Pennsylvania SIP because overall the
SIP will be stronger and more protective
of the environment with the
implementation of those measures by
Pennsylvania and because the SIP will
be stronger with federal approval and
enforceability of Pennsylvania’s RH SIP
than it would without those measures
being included in the Pennsylvania SIP.
EPA has already finalized the limited
disapproval of Pennsylvania’s RH SIP in
a separate rulemaking (77 FR 33642,
June 7, 2012). EPA is also approving this
revision as meeting the applicable
visibility related requirements of CAA
section 110(a)(2) including, but not
limited to, section 110(a)(2)(D)(i)(II) and
(a)(2)(J), relating to visibility protection
for the 1997 8-hour ozone NAAQS and
the 1997 and 2006 PM2.5 NAAQS.
PO 00000
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Fmt 4700
Sfmt 4700
41283
V. Statutory and Executive Order
Reviews
A. General Requirements
Under the CAA, the Administrator is
required to approve a SIP submission
that complies with the provisions of the
CAA and applicable Federal regulations.
42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions,
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this action
merely approves state law as meeting
Federal requirements and does not
impose additional requirements beyond
those imposed by state law. For that
reason, this action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
of Management and Budget under
Executive Order 12866 (58 FR 51735,
October 4, 1993);
• 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
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41284
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costs on tribal governments or preempt
tribal law.
B. Submission to Congress and the
Comptroller General
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing this action and other
required information to the U.S. Senate,
the U.S. House of Representatives, and
the Comptroller General of the United
States prior to publication of the rule in
the Federal Register. A major rule
cannot take effect until 60 days after it
is published in the Federal Register.
This action is not a ‘‘major rule’’ as
defined by 5 U.S.C. 804(2).
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 September 11, 2012. 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
finalizing the limited approval of the
Pennsylvania Regional Haze SIP may
not be challenged later in proceedings to
enforce its requirements. See section
307(b)(2) of the CAA.
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Incorporation by
reference, Nitrogen dioxide, Particulate
State
submittal
date
Name of non-regulatory SIP
revision
Applicable geographic area
*
*
Regional Haze Plan .................
*
Statewide ................................
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2011–0398; FRL–9352–2]
Azoxystrobin; Pesticide Tolerances
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This regulation establishes
tolerances for residues of azoxystrobin
in or on multiple commodities which
are identified and discussed later in this
document. Interregional Research
Project Number 4 (IR–4) and Syngenta
Crop Protection requested these
tolerances under the Federal Food,
Drug, and Cosmetic Act (FFDCA).
DATES: This regulation is effective July
13, 2012. Objections and requests for
hearings must be received on or before
September 11, 2012, and must be filed
in accordance with the instructions
provided in 40 CFR part 178 (see also
Unit I.C. of the SUPPLEMENTARY
INFORMATION).
tkelley on DSK3SPTVN1PROD with RULES
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12/20/10
FOR FURTHER INFORMATION CONTACT:
Andrew Ertman, Registration Division,
(7505P) Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave. NW., Washington,
DC 20460–0001; telephone number:
(703) 308–9367; email address:
ertman.andrew@epa.gov.
PO 00000
Frm 00038
Fmt 4700
Sfmt 4700
40 CFR part 52 is amended as follows:
PART 52—[AMENDED]
1. The authority citation for part 52
continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
Subpart NN— Pennsylvania
2. In § 52.2520, the table in paragraph
(e) is amended by adding an entry for
Regional Haze Plan at the end of the
table to read as follows:
■
§ 52.2020
*
Identification of plan.
*
*
(e)* * *
*
*
Additional explanation
*
*
*
7/13/12 [Insert page number
§ 52.2042; Limited Apwhere the document begins].
proval.
The docket for this action,
identified by docket identification (ID)
number EPA–HQ–OPP–2011–0398;
FRL–9352–2, is available either
electronically through https://
www.regulations.gov or in hard copy at
the OPP Docket in the Environmental
Protection Agency Docket Center (EPA/
DC), located in EPA West, Rm. 3334,
1301 Constitution Ave. NW.,
Washington, DC 20460–0001. The
Public Reading Room is open from
8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding legal holidays. The
telephone number for the Public
Reading Room is (202) 566–1744, and
the telephone number for the OPP
Docket is (703) 305–5805. Please review
the visitor instructions and additional
information about the docket available
at https://www.epa.gov/dockets.
SUPPLEMENTARY INFORMATION:
Dated: June 15, 2012.
W.C. Early,
Acting Regional Administrator, Region III.
EPA approval date
ADDRESSES:
[FR Doc. 2012–16428 Filed 7–12–12; 8:45 am]
SUMMARY:
*
matter, Reporting and recordkeeping
requirements, Sulfur oxides, Volatile
organic compounds.
I. General Information
A. Does this action apply to me?
You may be potentially affected by
this action if you are an agricultural
producer, food manufacturer, or
pesticide manufacturer. Potentially
affected entities may include, but are
not limited to those engaged in the
following activities:
• Crop production (NAICS code 111).
• Animal production (NAICS code
112).
• Food manufacturing (NAICS code
311).
• Pesticide manufacturing (NAICS
code 32532).
This listing is not intended to be
exhaustive, but rather to provide a guide
for readers regarding entities likely to be
affected by this action. Other types of
entities not listed in this unit could also
be affected. The North American
Industrial Classification System
(NAICS) codes have been provided to
assist you and others in determining
whether this action might apply to
certain entities. If you have any
questions regarding the applicability of
this action to a particular entity, consult
the person listed under FOR FURTHER
INFORMATION CONTACT.
E:\FR\FM\13JYR1.SGM
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Agencies
[Federal Register Volume 77, Number 135 (Friday, July 13, 2012)]
[Rules and Regulations]
[Pages 41279-41284]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2012-16428]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R03-OAR-2012-0002; FRL-9695-5]
Approval and Promulgation of Air Quality Implementation Plans;
Pennsylvania; Regional Haze State Implementation Plan
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: EPA is finalizing the limited approval of the Regional Haze
State Implementation Plan (SIP) (hereafter RH SIP) revision submitted
by the Commonwealth of Pennsylvania (Pennsylvania). EPA is taking this
action because Pennsylvania's SIP revision, as a whole, strengthens the
Pennsylvania SIP. This action is being taken in accordance with the
requirements of the Clean Air Act (CAA) and EPA's rules for states to
prevent and remedy future and existing anthropogenic impairment of
visibility in mandatory Class I areas
[[Page 41280]]
through a regional haze program. EPA is also approving this revision as
meeting the infrastructure requirements relating to visibility
protection for the 1997 8-hour ozone National Ambient Air Quality
Standard (NAAQS) and the 1997 and 2006 fine particulate matter
(PM2.5) NAAQS.
DATES: This final rule is effective on August 13, 2012.
ADDRESSES: EPA has established a docket for this action under Docket ID
Number EPA-R03-OAR-2012-0002. All documents in the docket are listed in
the www.regulations.gov Web site. Although listed in the electronic
docket, some information is not publicly available, i.e., 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 either electronically through www.regulations.gov or in hard
copy for public inspection during normal business hours at the Air
Protection Division, U.S. Environmental Protection Agency, Region III,
1650 Arch Street, Philadelphia, Pennsylvania 19103. Copies of the
Commonwealth's submittal are available at the Pennsylvania Department
of Environmental Protection, Bureau of Air Quality Control, P.O. Box
8468, 400 Market Street, Harrisburg, Pennsylvania 17105.
FOR FURTHER INFORMATION CONTACT: Melissa Linden, (215) 814-2096, or by
email at linden.melissa@epa.gov.
SUPPLEMENTARY INFORMATION:
I. Background
Throughout this document, whenever ``we,'' ``us,'' or ``our'' is
used, we mean EPA. On January 26, 2012, EPA published a notice of
proposed rulemaking (NPR) for Pennsylvania (77 FR 3984). The NPR
proposed limited approval of Pennsylvania's RH SIP. The formal SIP
revision was submitted by the Pennsylvania Department of Environmental
Protection (PADEP) on December 20, 2010. This revision also meets the
requirements of CAA section 110(a)(2)(D)(i)(II) and (a)(2)(J), relating
to visibility protection for the 1997 8-hour ozone NAAQS and the 1997
and 2006 PM2.5 NAAQS.
II. Summary of SIP Revision
The SIP revision includes a long term strategy with enforceable
measures ensuring reasonable progress towards meeting the reasonable
progress goals for the first planning period through 2018.
Pennsylvania's RH SIP contains the emission reductions needed to
achieve Pennsylvania's share of emission reductions for the Class I
areas they impact. The specific requirements of the CAA and EPA's
Regional Haze Rule (64 FR 35714, July 1, 1999) and the rationale for
EPA's proposed action are explained in the NPR and are not restated
here. EPA received several adverse comments and one letter of support
on the January 26, 2012 NPR. One of those adverse comments requested a
change to PADEP's best available retrofit technology (BART)
determination for GenOn Energy's Cheswick Generating Station.
Pennsylvania can revise this determination in a future SIP revision to
address comments raised by GenOn Energy. A summary of the comments
submitted and EPA's responses are provided in section III of this
document.
III. Summary of Public Comments and EPA Responses
Comment: EPA proposed approval of Pennsylvania's RH SIP on January
26, 2012 with a docket that includes most of the RH SIP submission from
PADEP except Appendix Z, which is the comment and response document.
Response: PADEP did not submit an Appendix Z, nor was it referenced
in the rulemaking. The PADEP comment and response document is Appendix
AA and can be found in the EPA docket for this action, docket No. EPA-
R03-OAR-2012-0002.
Comment: The commenter stated that Pennsylvania has 15 BART-
eligible electric generating units (EGUs) that include 28 individual
units that are among the largest uncontrolled sources for nitrogen
oxides (NOX) and sulfur dioxide (SO2). The
commenter claimed PADEP did not conduct any five-step determinations
for BART at these EGUs for NOX and SO2. It relied
upon the pending ``cross state air pollution rule (CSAPR) Better than
BART'' determination.
Response: In today's action, EPA is finalizing a limited approval
of Pennsylvania's RH SIP based on its reliance on the Clean Air
Interstate Rule (CAIR). EPA did not propose to find that participation
in the Transport Rule\1\ is an alternative to BART in this action. EPA
addressed these comments concerning the Transport Rule as a BART
alternative in a final action that was published on June 7, 2012 (77 FR
33642). EPA's response to these comments can be found in Docket ID No.
EPA-HQ-OAR-2011-0729 at www.regulations.gov.
---------------------------------------------------------------------------
\1\ The Transport Rule is also known as the Cross State Air
Pollution Rule (CSAPR) and was proposed by EPA to help states reduce
air pollution and attain CAA standards. See 75 FR 45210 (August 2,
2010) (proposal) and 76 FR 48208 (August 8, 2011) (final rule).
---------------------------------------------------------------------------
Comment: The commenter stated that BART determinations must
consider filterable PM10, PM2.5 and condensable
PM. The commenter stated that the PADEP BART determinations are
expressed in total PM, but the cost analyses were conducted based on
filterable PM10. The commenter requested EPA to disapprove
PADEP's determinations and adopt a FIP that establishes BART limits for
filterable PM10, PM2.5 and condensable PM because
PADEP set BART limits for filterable PM10 and filterable PM.
Response: EPA disagrees with the commenter that the PM BART limits
should be disapproved. The controls on the facilities considered by
PADEP for the emission limits in the BART determinations are effective
in reducing filterable and condensable particulates. Separate emission
limits for each are not required for BART.
Comment: The commenter claimed PADEP's BART determinations and
EPA's proposed approval of these determinations are fundamentally
flawed, arbitrary, and unlawful. The commenter stated that source-
specific process design information is required to make BART
determinations which PADEP did not provide. One commenter stated
PADEP's BART determinations were fundamentally flawed for steps one
through four of the BART determination process. The commenter stated
the flaw in step one was that PADEP did not address all available
technologies for each BART determination. The commenter stated the flaw
in step two was that PADEP did not appropriately interpret technical
feasibility of control options in accordance with the Guidelines for
BART Determinations under the Regional Haze Rule at Appendix Y to 40
CFR part 51 (hereafter the BART Rule). See 70 FR 39104 (July 6, 2005).
The commenter stated the flaw in step three was that PADEP did not rank
the control effectiveness for all EGU and most non-EGU BART
determinations. The commenter stated the flaw in step four was that
PADEP eliminated technologies based on non-air quality environmental
impacts that are common throughout the industry.
Response: Congress crafted the CAA to provide for states to take
the lead in developing implementation plans but balanced that decision
by requiring EPA to review the plans to determine whether a SIP meets
the requirements of the CAA. In undertaking such a review, EPA does not
usurp a state's authority
[[Page 41281]]
but ensures that such authority is reasonably exercised. BART
determinations under the regional haze program are the responsibility
of the states, which have the freedom to determine the weight and
significance of the statutorily required five-factors in a BART
determination. EPA then reviews a state's determination as included in
its regional haze plan. Pennsylvania performed the required BART
determinations for its BART-eligible sources. In Appendix J of its RH
SIP submittal, Pennsylvania considered the required five-factors and
explained its conclusions for each specific source. As identified in
Appendix J, Pennsylvania performed its BART determinations evaluating
the five-factors required. Appendix J describes the steps Pennsylvania
took in evaluating BART and provides a basis for Pennsylvania's BART
determinations based on those five- factors. The modeling of source
impacts and technology reviews for specific source categories can be
found in Pennsylvania's Appendices I, P and Q respectively, which
support Pennsylvania's BART determinations found in Appendix J. EPA
determined that PADEP did address all available technologies and
appropriately determined technical feasibility of those technologies.
The ranking of control technologies is not a requirement of step three
(evaluating the control effectiveness) in BART determinations. The
evaluation of non-air quality impacts as part of step four of the BART
determination should be made based on a consideration of the specific
circumstances of that source, so the same technology may have a
different degree of impact dependent on the source. EPA determined that
PADEP did address step four for the BART determinations in accordance
with the BART Rule.
Comment: The commenter stated that the PM limit for EGUs is invalid
for BART. Pennsylvania used an outdated 0.1 pound per million British
thermal unit (lb/MMBtu) limit for filterable PM. The proposed BART
limit is much higher than accepted as BART (or as best available
control technology known as BACT), and much higher than levels
currently being achieved at many other similar facilities.
Response: EPA disagrees that the PM BART limits are invalid. While
BACT is similar to BART, BACT has a four factor analysis of
environmental impact, energy consumption, economic impact, and other
costs. BART determinations however involve a five factor analysis of
all technologies available for retrofit, consideration of current
control technologies, cost of compliance of controls, remaining useful
life of the facility, energy and non air-quality environmental impacts,
and visibility impacts. BART is not a required top-down evaluation like
BACT. As stated in the BART Rule, the states should retain the
discretion to evaluate control options in whatever order they choose,
so long as the state explains its analysis of the CAA factors. PADEP
did address each of the five factors in its BART determination
summaries in Appendix J of the PADEP December 20, 2010 RH SIP
submittal. Because BART and BACT involve different evaluations, EPA
believes it is reasonable to have different outcomes and different
limits for each review. The specific BACT limits cited by the commenter
cannot automatically be considered valid for BART.
Comment: BART guidelines provide that maximum available control
technology (MACT) for hazardous air pollutants (HAPs) should be taken
into account for determining BART as stated in 40 CFR part 51, appendix
Y, Section IV.C. The commenter stated that Pennsylvania EGUs are
subject to EPA's Mercury and Air Toxics Standards (MATS Rule) which was
published on February 16, 2012 (77 FR 9304). The commenter stated that
EPA must take these requirements into account in approving any BART
determination because all statutory factors should be included. The
commenter stated that PADEP's BART determinations for PM limits of 0.1
lb/MMBtu cannot be approved because those limits are much higher than
the 0.03 lb/MMBtu limit in the final MATS Rule as a surrogate limit for
non-mercury metal HAPs.
Response: EPA agrees that we do require all statutory factors to be
included in the BART determinations that are applicable at the time the
determinations are done. EPA cannot require BART determinations to
predict future requirements and to include those as BART. When EPA
issues new rules, the states must adopt them as appropriate. The final
MATS Rule was promulgated after the proposed limited approval of the PM
BART determinations in the Pennsylvania RH SIP on January 26, 2012.
Comment: The commenter stated that EPA claimed it included all
BART-eligible sources in the CSAPR Better-than-BART analysis, but the
analysis omitted the BART-eligible oil-fired EGUs as identified by
PADEP. These facilities in Pennsylvania are Trigen/Edison Station Units
3 and 4; Trigen/Schuylkill Station Unit 26; Eddystone Units 3 and 4;
and Martins Creek Units 3 and 4. EPA's CSAPR Better-than-BART analysis
compared projected EGU emissions at the presumptive EGU BART limits to
projected emissions under CSAPR. EPA then modeled these scenarios
against the 2014 baseline that excludes both BART and CSAPR. The
visibility benefits from this modeling were then averaged across all
Class I areas. The commenter stated that EPA claims this analysis shows
that CSAPR will result in more emissions reductions than BART and cites
to 76 FR 82225. The commenter claimed that CSAPR will not achieve
greater reasonable progress toward the national visibility goal than
source-specific BART for EGUs in Pennsylvania. Even if CSAPR could
lawfully substitute for BART, the commenter claimed the instant
rulemaking would have to include separate NOX and
SO2 BART determinations for Pennsylvania EGUs because CSAPR
does not in fact perform better than BART.
Response: These comments are beyond the scope of this rulemaking.
EPA's response to comments concerning the ``CSAPR is Better-than-BART''
action can be found in Docket ID No. EPA-HQ-OAR-2011-0729 at
www.regulations.gov.
Comment: The commenter stated that PADEP evaluated step five of the
BART determinations in a piecemeal fashion, considering the visibility
impact to each Class I area separately and determined controls based on
the most highly impacted Class I area. PADEP's approach resulted in
significantly underestimating visibility improvements compared to
implementing BART for PA sources. Most of the BART-eligible sources are
clustered in the southwest corner of the state, near four Class I
areas. Most of the remaining BART-eligible sources are clustered in the
southeast region of the state, near Brigantine Class I area, with
Montour in the middle of the state. The federal land managers (FLMs)
made similar comments on the draft Pennsylvania RH SIP. PADEP responded
that the BART Rule does not require a ``cumulative'' impact analysis
and stated that EPA has provided no guidance on this issue. The
commenter disagreed and stated that the BART Rule is clear that
multiple sources and Class I areas are to be considered. The commenter
cited to 70 FR 39161-62. The commenter claimed EPA recommended that
Nebraska Department of Environmental Quality (NDEQ) consider
calculating the visibility improvement at multiple Class I areas.
Response: EPA disagrees with this comment in general. The BART Rule
pages referred to by the commenter
[[Page 41282]]
address determining whether a facility is BART-eligible and not the
applicable approach defined later in the guidelines for BART-subject
sources. EPA agrees with PADEP that the BART Rule does not require a
``cumulative'' impact analysis as part of the BART determination for a
specific source. The guidelines do give the option to evaluate
cumulative impacts to multiple Class I areas which EPA does recommend
but does not require the state to do. As noted by the language used by
EPA to NDEQ, we recommend consideration of the cumulative approach.
Comment: The commenter stated that the PADEP source-specific
analyses in Appendix J rejected every single control option as not cost
effective using one or both of the following two measures: dollar per
ton or dollar per deciview. However, no significance thresholds were
established for either. The FLMs also commented on this issue during
the PADEP review process. PADEP's response to the FLMs was that it did
not establish or use ``bright line thresholds for cost or for
visibility improvement in making BART determinations'' in Appendix AA
of the Pennsylvania RH SIP submittal. The commenter noted that based on
determinations in other states, the acceptable cost effectiveness value
ranges from $5,000 per ton to $10,000 per ton. The commenter claimed
that many of PADEP's ``no control'' determinations fall well below this
range.
Response: EPA's BART guidelines in the BART Rule do not require
Pennsylvania to develop a specific threshold, but rather to evaluate
each BART determination on a case-by-case basis for each source. EPA
has not established a specific cost threshold that makes a particular
control option BART based on just a dollars per ton number. All five
factors must be compared to determine the level of control that is BART
on a case-by-case basis. As discussed in the NPR, EPA finds the BART
determinations from PADEP reasonable.
Comment: The commenter stated that EPA unreasonably relies on CSAPR
for BART and that EPA failed to adequately review Pennsylvania's BART
determinations.
Response: For BART determinations of sources other than EGUs, EPA
reviewed PADEP's BART determinations in the December 20, 2010
Pennsylvania RH SIP submittal and approves the conclusions as the
determinations are reasonable. Comments related to CSAPR as an
alternative to BART for EGUs are beyond the scope of this rulemaking.
EPA addressed similar comments concerning the Transport Rule as a BART
alternative in a final action that was signed on May 30, 2012 (77 FR
33642, June 7, 2012). The EPA's response to these comments can be found
in Docket ID No. EPA-HQ-OAR-2011-0729 at www.regulations.gov.
Comment: The commenter stated that EPA's proposed SO2
reductions from Pennsylvania sources as substitute measures addressing
Pennsylvania's failure to adopt the Mid-Atlantic/Northeast Visibility
Union (MANE-VU) low sulfur fuel oil strategy are largely reliant upon
the Portland Generating Station SO2 reductions from the
federally enforceable order from EPA responding to the CAA section 126
petition from the State of New Jersey. The commenter also states that
this order has been appealed in the federal Court of Appeals and should
not be relied upon due to its uncertainty.
Response: EPA disagrees with the commenter. The rule issued in
response to the CAA section 126 petition from the State of New Jersey
for the Portland Generating Station is federally enforceable and can be
relied upon because it has not been stayed, nor has it been revoked at
this time. The reductions can be relied upon for reasonable progress at
this time because it is a federally enforceable measure. If these
reductions do not occur, then PADEP may have to address them in the
five year look back by submitting a SIP revision.
Comment: The commenter stated that Pennsylvania's failure to adopt
the low-sulfur fuel oil strategy that was included in New Jersey's
reasonable progress goals cannot be supplemented by SO2
emission reductions without modeling the impacts as required by 40 CFR
51.308(d)(3)(iii).
Response: EPA disagrees with the commenter. 40 CFR
51.308(d)(3)(iii) provides that a state ``must document the technical
basis, including modeling, monitoring and emissions information, on
which the State is relying to determine its apportionment of emission
reduction obligations necessary for achieving reasonable progress in
each mandatory Class I Federal area it affects. The State may meet this
requirement by relying on technical analyses developed by the RPO and
approved by all State participants. The State must identify the
baseline emissions inventory on which its strategies are based.'' 40
CFR 51.308(d)(3)(iii). EPA did identify the baseline emissions for the
measures substituted to address the SO2 reductions that
would have come from Pennsylvania's low-sulfur fuel oil strategy, and
the modeling impact of the MANE-VU rule was done by the regional
planning organization (RPO). The low-sulfur fuel oil strategy was an
area source rule and the substituted emission reductions are from
specific sources that are located closer to the Brigantine Class I
area. Thus, the substitution of SO2 reductions does meet the
requirements in 40 CFR 51.308(d)(3)(iii).
Comment: The commenter stated that both the EPA proposed action for
CSAPR Better-than-BART and EPA's proposed action on Pennsylvania's RH
SIP stated that EPA was taking action on long-term strategy in a
separate notice. The commenter stated that neither rulemaking acted on
the long-term strategy for Pennsylvania which is untenable according to
the commenter.
Response: The commenter has made an incorrect assumption. The EPA
stated in the proposed action for CSAPR Better-than-BART that we
proposed a limited disapproval of the regional haze SIPs that have been
submitted by several states including Pennsylvania and that these
states ``fully consistent with the EPA's regulations at the time,
relied on CAIR requirements to satisfy the BART requirement and the
requirement for a long-term strategy sufficient to achieve the state-
adopted reasonable progress goals'' (76 FR 82221). We further stated
that ``CAIR and CAIR FIP requirements, however, will only remain in
force to address emissions through the 2011 control period and thus
CAIR cannot be relied upon in a SIP as a substitute for BART or as part
of a long-term control strategy.'' Id. EPA proposed and finalized a
limited disapproval for the Pennsylvania RH SIP for the long-term
strategy due to reliance on CAIR. The other long-term strategy measures
are covered under the limited approval proposed for Pennsylvania's RH
SIP in 77 FR 3988. Therefore, all long-term control strategies beyond
reliance on CAIR are included in the limited approval previously
proposed, and now finalized, by this action. The final limited
disapproval and FIP was published on June 7, 2012, addressing the
deficiencies of the long-term strategy insofar as it relied on CAIR (77
FR 33642).
Comment: The commenter requested a conditional approval of
Pennsylvania's RH SIP requiring the implementation of the lower-sulfur
fuel strategy since it was relied upon for establishing the reasonable
progress goals for MANE-VU Class I areas. Multiple commenters also
stated that EPA's substitution of emission reductions is not permitted
under the
[[Page 41283]]
Regional Haze Rule for reasonable progress goals for visibility.
Response: EPA does not agree that a conditional approval is
appropriate for the Pennsylvania RH SIP given our determination that
the plan meets the relevant applicable requirements. As set forth in a
prior response, EPA disagrees that substitution of emission reductions
is not permitted for reasonable progress goals.
Comment: The commenter stated that EPA should have disapproved
Pennsylvania's RH SIP due to PADEP's failure to implement a proposed
low-sulfur fuel oil strategy. The commenter stated that EPA should have
demanded the additional 5,702 tons of SO2 emission
reductions from Pennsylvania instead of saying that EPA does not
anticipate the difference will interfere with the ability of other
states to achieve reasonable progress goals.
Response: EPA disagrees with the commenter. Disapproving the entire
Pennsylvania RH SIP would have slowed implementation of other controls
listed in the RH SIP. As explained in the NPR, we anticipate that the
Pennsylvania RH SIP will ensure sufficient emission reductions to meet
its share needed for nearby states to achieve their reasonable progress
goals. If it is determined that the shortfall of SO2
emission reductions impedes the achievement of reasonable progress,
then at the time of the five year periodic review PADEP may need to
submit a SIP revision requiring those additional reductions.
Comment: One commenter stated that the PADEP BART determination for
GenOn Energy's Cheswick Generating Station included emission limits
including PM which were inconsistent with the plant's current permits.
The commenter requested EPA to require PADEP to revise the BART
determination.
Response: EPA evaluated the BART determination and agrees with
PADEP's determination of the appropriate BART limit based on current
controls. In setting the BART limits, PADEP appears to have set
emission limits for the facility that are far more stringent than
intended. If Pennsylvania submits a revised BART determination for the
Cheswick Generating Station, EPA commits to act expeditiously on the
revised SIP submittal.
Comment: Two commenters stated that PADEP did not address
reasonable progress requirements for addressing MANE-VU's modeled
exceedance of the uniform rate of progress (URP) at Dolly Sods Class I
area.
Response: Reasonable progress goals are set by the Class I area
state. West Virginia did not request any reductions from Pennsylvania
to meet the URP as modeled by Visibility Improvement State and Tribal
Association of the Southeast (VISTAS). The discrepancies in modeling
between the two RPOs were addressed in Pennsylvania's RH SIP submittal.
The requirement for the state consultation process was met, and
Pennsylvania fulfilled what was requested by West Virginia.
Comment: The commenter stated that Pennsylvania's modeling for the
RH SIP submittal did not address the significant growth in emissions
from Marcellus Shale natural gas drilling operations and therefore does
not support reasonable progress.
Response: EPA disagrees with the commenter because reasonable
progress goals are set by the Class I area and are evaluated during the
5 year periodic review. In addition, CAA section 169A(g)(1) requires
states to take into consideration a number of factors for reasonable
progress. States have flexibility in how to take into consideration
these statutory factors and any other factors that are determined to be
relevant. As previously explained herein and in the NPR, we anticipate
that the Pennsylvania RH SIP will ensure sufficient emission reductions
for reasonable progress goals. During the five year periodic review,
any significant changes in projected emissions can be addressed.
IV. Final Action
EPA is finalizing its limited approval of the revision to the
Pennsylvania SIP submitted on December 20, 2010 that addresses regional
haze for the first implementation period in Pennsylvania. EPA is
issuing a limited approval of the Pennsylvania SIP because overall the
SIP will be stronger and more protective of the environment with the
implementation of those measures by Pennsylvania and because the SIP
will be stronger with federal approval and enforceability of
Pennsylvania's RH SIP than it would without those measures being
included in the Pennsylvania SIP. EPA has already finalized the limited
disapproval of Pennsylvania's RH SIP in a separate rulemaking (77 FR
33642, June 7, 2012). EPA is also approving this revision as meeting
the applicable visibility related requirements of CAA section 110(a)(2)
including, but not limited to, section 110(a)(2)(D)(i)(II) and
(a)(2)(J), relating to visibility protection for the 1997 8-hour ozone
NAAQS and the 1997 and 2006 PM2.5 NAAQS.
V. Statutory and Executive Order Reviews
A. General Requirements
Under the CAA, the Administrator is required to approve a SIP
submission that complies with the provisions of the CAA and applicable
Federal regulations. 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in
reviewing SIP submissions, EPA's role is to approve state choices,
provided that they meet the criteria of the CAA. Accordingly, this
action merely approves state law as meeting Federal requirements and
does not impose additional requirements beyond those imposed by state
law. For that reason, this action:
Is not a ``significant regulatory action'' subject to
review by the Office of Management and Budget under Executive Order
12866 (58 FR 51735, October 4, 1993);
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
[[Page 41284]]
costs on tribal governments or preempt tribal law.
B. Submission to Congress and the Comptroller General
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report, which includes a copy of the rule,
to each House of the Congress and to the Comptroller General of the
United States. EPA will submit a report containing this action and
other required information to the U.S. Senate, the U.S. House of
Representatives, and the Comptroller General of the United States prior
to publication of the rule in the Federal Register. A major rule cannot
take effect until 60 days after it is published in the Federal
Register. This action is not a ``major rule'' as defined by 5 U.S.C.
804(2).
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 September 11, 2012. 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 finalizing the limited approval of the Pennsylvania
Regional Haze SIP may not be challenged later in proceedings to enforce
its requirements. See section 307(b)(2) of the CAA.
List of Subjects in 40 CFR Part 52
Environmental protection, Air pollution control, Incorporation by
reference, Nitrogen dioxide, Particulate matter, Reporting and
recordkeeping requirements, Sulfur oxides, Volatile organic compounds.
Dated: June 15, 2012.
W.C. Early,
Acting Regional Administrator, Region III.
40 CFR part 52 is amended as follows:
PART 52--[AMENDED]
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. 52.2520, the table in paragraph (e) is amended by adding an
entry for Regional Haze Plan at the end of the table to read as
follows:
Sec. 52.2020 Identification of plan.
* * * * *
(e)* * *
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State
Name of non-regulatory SIP revision Applicable geographic submittal EPA approval date Additional explanation
area date
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* * * * * * *
Regional Haze Plan.................... Statewide................ 12/20/10 7/13/12 [Insert page Sec. 52.2042; Limited Approval.
number where the
document begins].
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[FR Doc. 2012-16428 Filed 7-12-12; 8:45 am]
BILLING CODE 6560-50-P