Air Quality Implementation Plan Approval; Illinois; Illinois Power Holdings and AmerenEnergy Medina Valley Cogen Variance, 79261-79266 [2015-31882]
Download as PDF
Federal Register / Vol. 80, No. 244 / Monday, December 21, 2015 / Rules and Regulations
This deviation is effective from
5 a.m. to 10:30 a.m. on Sunday, March
20, 2016.
ADDRESSES: The docket for this
deviation, [USCG–2015–1064] is
available at https://www.regulations.gov.
Type the docket number in the
‘‘SEARCH’’ box and click ‘‘SEARCH’’.
Click on Open Docket Folder on the line
associated with this deviation.
FOR FURTHER INFORMATION CONTACT: If
you have questions on this temporary
deviation, call or email Kashanda
Booker, Bridge Administration Branch,
Fifth Coast Guard; telephone 757–398–
6227, email Kashanda.l.booker@
uscg.mil.
SUPPLEMENTARY INFORMATION: The 7th
Annual Quintiles Wrightsville Beach
Marathon committee on behalf of the
North Carolina Department of
Transportation (NCDOT) has requested
a temporary deviation from the current
operating schedule for the SR 74
Bascule Drawbridge across the AIWW,
mile 283.1, at Wrightsville Beach, NC.
The requested deviation will
accommodate the 7th Annual Quintiles
Wrightsville Beach Marathon scheduled
for Sunday, March 20, 2016. To
facilitate this event, the draw of the
bridge will be maintained in the closedto-navigation position from 5 a.m. to
10:30 a.m. to allow race participants to
cross during the scheduled event.
The current operation schedule is set
out in 33 CFR 117.821(a)(4). The
regulation requires the bridge to open
on signal for vessels at all times except
that from 7 a.m. until 7 p.m. the bridge
shall open on the hour; every third and
fourth Saturday in September the bridge
shall remain closed from 7 a.m. until 11
a.m.; and the last Saturday of October or
the first or second Saturday of
November the bridge shall remain
closed from 7 a.m. until 10:30 a.m. The
bascule drawbridge has a vertical
clearance of 20 feet above mean high
water (MHW) in the closed position.
Vessels able to pass through the
bridge in the closed position may do so
at anytime. The bridge will be able to
open for emergencies and there is no
immediate alternate route for vessels.
Most waterway traffic consists of
recreational boats with a few barges and
tugs during the daytime. The Coast
Guard will also inform the users of the
waterways through our Local and
Broadcast Notices to Mariners of the
change in operating schedule for the
bridge so that vessel operators can
arrange their transits to minimize any
impact caused by the temporary
deviation.
In accordance with 33 CFR 117.35(e),
the drawbridge must return to its regular
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DATES:
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operating schedule immediately at the
end of the effective period of this
temporary deviation. This deviation
from the operating regulations is
authorized under 33 CFR 117.35.
Dated: December 15, 2015.
Hal R. Pitts,
Bridge Program Manager, Fifth Coast Guard
District.
[FR Doc. 2015–31938 Filed 12–18–15; 8:45 am]
BILLING CODE 9110–04–P
DEPARTMENT OF HOMELAND
SECURITY
Coast Guard
33 CFR Part 117
[Docket No. USCG–2015–1063]
Drawbridge Operation Regulation;
Connecticut River, Old Lyme, CT
Coast Guard, DHS.
Notice of deviation from
drawbridge regulation.
AGENCY:
ACTION:
The Coast Guard has issued a
temporary deviation from the operating
schedule that governs the Amtrak Old
Saybrook-Old Lyme Bridge across the
Connecticut River, mile 3.4, at Old
Lyme, Connecticut. This deviation is
necessary to perform gear box
replacement. This deviation allows the
bridge to remain in the closed position
for approximately 5 days.
DATES: This deviation is effective from
7:00 a.m. on January 25, 2016 to 7:00
a.m. on February 6, 2016.
ADDRESSES: The docket for this
deviation, [USCG–2015–1063] is
available at https://www.regulations.gov.
Type the docket number in the
‘‘SEARCH’’ box and click ‘‘SEARCH’’.
Click on Open Docket Folder on the line
associated with this deviation.
FOR FURTHER INFORMATION CONTACT: If
you have questions on this temporary
deviation, call or email Ms. Judy K.
Leung-Yee, Project Officer, First Coast
Guard District, telephone (212) 514–
4330, email judy.k.leung-yee@uscg.mil.
SUPPLEMENTARY INFORMATION: National
Passenger Railroad Corporation
(Amtrak) requested this temporary
deviation from the normal operating
schedule to perform gear box
replacement.
The Amtrak Old Saybrook-Old Lyme
Bridge, mile 3.4, across the Connecticut
River has a vertical clearance in the
closed position of 19 feet at mean high
water and 22 feet at mean low water.
The existing bridge operating
regulations are found at 33 CFR
117.205(b).
SUMMARY:
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79261
The waterway is transited by one
commercial user and recreation vessel
traffic.
Under this temporary deviation, the
Amtrak Old Saybrook-Old Lyme Bridge
may remain in the closed position from
7:00 a.m. on January 25, 2016 to 7:00
a.m. on January 30, 2016 with rain date
from 7:00 a.m. on February 1, 2016 to
7:00 a.m. on February 6, 2016.
Vessels able to pass through the
bridge in the closed positions may do so
at anytime. The bridge will not be able
to open for emergencies and there is no
immediate alternate route for vessels to
pass.
The Coast Guard will also inform the
users of the waterways through our
Local and Broadcast Notices to Mariners
of the change in operating schedule for
the bridge so that vessels can arrange
their transits to minimize any impact
caused by the temporary deviation.
In accordance with 33 CFR 117.35(e),
the drawbridge must return to its regular
operating schedule immediately at the
end of the effective period of this
temporary deviation. This deviation
from the operating regulations is
authorized under 33 CFR 117.35.
Dated: December 15, 2015.
C.J. Bisignano,
Supervisory Bridge Management Specialist,
First Coast Guard District.
[FR Doc. 2015–31939 Filed 12–18–15; 8:45 am]
BILLING CODE 9110–04–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R05–OAR–2014–0705; FRL–9939–75–
Region 5]
Air Quality Implementation Plan
Approval; Illinois; Illinois Power
Holdings and AmerenEnergy Medina
Valley Cogen Variance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
The Environmental Protection
Agency (EPA) is approving into the
Illinois Regional Haze State
Implementation Plan (SIP) a variance for
the electrical generating units (EGUs)
included in the Ameren Multi-Pollutant
Standard Group (Ameren MPS Group).
The Ameren MPS Group consists of five
facilities owned by Illinois Power
Holdings, LLC (IPH) and two facilities
owned by AmerenEnergy Medina Valley
Cogen, LLC (Medina Valley). The
Illinois Environmental Protection
Agency (IEPA) submitted the variance to
EPA for approval on September 3, 2014.
SUMMARY:
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This final rule is effective on
January 20, 2016.
ADDRESSES: EPA has established a
docket for this action under Docket ID
No. EPA–R05–OAR–2014–0705. All
documents in the docket are listed on
the www.regulations.gov Web site.
Although listed in the index, 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 at
the Environmental Protection Agency,
Region 5, Air and Radiation Division, 77
West Jackson Boulevard, Chicago,
Illinois 60604. This facility is open from
8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding Federal holidays. We
recommend that you telephone
Kathleen D’Agostino, Environmental
Engineer, at (312) 886–1767 before
visiting the Region 5 office.
FOR FURTHER INFORMATION CONTACT:
Kathleen D’Agostino, Environmental
Engineer, Attainment Planning and
Maintenance Section, Air Programs
Branch (AR–18J), Environmental
Protection Agency, Region 5, 77 West
Jackson Boulevard, Chicago, Illinois
60604, (312) 886–1767,
dagostino.kathleen@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document whenever
‘‘we,’’ ‘‘us,’’ or ‘‘our’’ is used, we mean
EPA. This supplementary information
section is arranged as follows:
DATES:
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I. Background
II. Response to Comments
III. Final Action
IV. Incorporation by Reference
V. Statutory and Executive Order Reviews
I. Background
On June 24, 2011, Illinois submitted
a plan to address the requirements of
the Regional Haze Rule, as codified at
40 CFR 51.308. EPA approved Illinois’
Regional Haze SIP on July 6, 2012 (77
FR 39943). In its approval, EPA
determined that the emission reductions
from sources included in the Illinois
plan are significantly greater than even
conservative definitions of best
available retrofit technology (BART)
applied to BART subject units. Id. at
39946. EPA also addressed whether the
Illinois plan can also be expected to
achieve greater visibility protection than
application of BART on BART-subject
units. Given that, in general, the Illinois
power plants are substantial distances
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from any Class I area, and given that the
averaging in Illinois’ plan is only
authorized within the somewhat limited
region within which each utility’s
plants are located, EPA determined that
a reallocation of emission reductions
from one plant to another is unlikely to
change the visibility impact of those
emission reductions significantly.
Consequently, EPA concluded that the
significantly greater emission reductions
that Illinois required in its Regional
Haze SIP will yield greater progress
toward visibility protection as compared
to the benefits of a conservative estimate
of BART.
One of the rules approved in that
action to meet BART requirements is 35
Illinois Administrative Code (Ill. Adm.
Code) rule 225.233, Multi-Pollutant
Standard (MPS), specifically
subsections (a), (b), (e), and (g). Section
225.233(e)(3)(C) contains the sulfur
dioxide (SO2) emission standards
applicable to the Ameren MPS Group.
Section 225.233(e)(3)(C)(i) establishes
an overall SO2 annual emission rate for
EGUs in the Ameren MPS group of 0.50
pounds per million Btu (lb/mmBtu) for
calendar years 2010 through 2013.
Section 225.233(e)(3)(C)(ii) establishes
an overall SO2 annual emission rate for
EGUs in the Ameren MPS group of 0.43
lb/mmBtu for calendar year 2014.
Section 225.233(e)(3)(C)(iii) establishes
an overall SO2 annual emission rate for
EGUs in the Ameren MPS group of 0.25
lb/mmBtu for calendar years 2015 and
2016. Section 225.233(e)(3)(C)(iv)
establishes an overall SO2 annual
emission rate for EGUs in the Ameren
MPS group of 0.23 lb/mmBtu beginning
in calendar year 2017 and continuing
each calendar year thereafter.
On November 21, 2013, the Illinois
Pollution Control Board (IPCB) granted
IPH and Medina Valley a variance from
the applicable requirements of Section
225.233(e)(3)(C)(iii) for a period
beginning January 1, 2015, through
December 31, 2019, and Section
225.233(e)(3)(C)(iv) for a period
beginning January 1, 2017, through
December 31, 2019, subject to certain
conditions. The IPH facilities included
in the Ameren MPS Group and subject
to the variance are Coffeen Energy
Center (Montgomery County), Duck
Creek Energy Center (Fulton County),
E.D. Edwards Energy Center (Peoria
County), Joppa Energy Center (Massac
County), and Newton Energy Center
(Jasper County). The Medina Valley
facilities included in the Ameren MPS
Group and subject to the variance are
the Meredosia Energy Center (Morgan
County) and the Hutsonville Energy
Center (Crawford County). IEPA
submitted the variance as a revision to
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the Illinois Regional Haze SIP on
September 3, 2014.
EPA proposed to approve the variance
on April 20, 2015 (80 FR 21681). As
discussed in the proposal, the variance
results in less SO2 emissions than the
currently approved Regional Haze SIP.
Id. at 21683. In addition, EPA
determined that the significantly lower
SO2 emissions under the variance
versus application of Best Available
Control Technology (BACT) to BARTsubject sources, will yield greater
progress toward visibility protection. Id.
at 21684. Finally, with respect to the
requirements of section 110(l) of the
Clean Air Act (CAA) (42 U.S.C. 7410(l)),
because the variance will result in less
SO2 emissions than the currently
approved Regional Haze SIP and will
continue to provide better visibility
protection than the application of BART
to BART-subject units, EPA has
determined that the variance will not
interfere with attainment, reasonable
further progress, or any other applicable
requirement of the CAA. Id. at 21684.
II. Response to Comments
EPA received joint adverse comments
from Earthjustice and Sierra Club, as
summarized in the comments/responses
below.
Comment 1: The proposed SIP
revision unlawfully substitutes fleetwide emission limits for the unitspecific five factor BART analysis
required by the CAA.
Response 1: Section 169A(b)(2)(A) of
the CAA, 42 U.S.C. 7491(b)(2)(A),
requires states to revise their SIPs to
contain such measures as may be
necessary to make reasonable progress
towards the natural visibility goal,
including a requirement that certain
existing major stationary sources
procure, install, and operate BART, as
determined by the state. In some cases,
this requirement is met with an analysis
of potential controls for each source
subject to BART considering five factors
set out in EPA’s regional haze rule. 40
CFR 51.308(e)(1)(ii)(A). However, as
described in several previous rules, EPA
has concluded that CAA section 169A
may reasonably be interpreted to
provide that the requirement for BART
may be satisfied by an alternate program
that provides greater reasonable
progress toward visibility improvement
than direct application of BART to
individual sources determined to be
subject to the BART requirement. See 40
CFR 51.308(e), 64 FR 35714, 35741–
35743 (July 1, 1999), 70 FR 39104,
39136 (July 6, 2005), 71 FR 60612
(October 13, 2006), and 77 FR 33642
(June 7, 2012).
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In 1999, EPA promulgated the
Regional Haze Rule, which established
a comprehensive visibility protection
program for mandatory Class I Federal
areas (including many national parks
and wilderness areas). In the preamble
to the Regional Haze Rule, EPA stated
that, to demonstrate that emission
reductions of an alternative program
would result in greater emission
reductions, ‘‘the State must estimate the
emission reductions that would result
from the use of BART-level controls. To
do this, the State could undertake a
source-specific review of the sources in
the State subject to BART, or it could
use a modified approach that simplifies
the analysis.’’ 64 FR 35742 (July 1,
1999).
In a final rule revising certain
provisions of the Regional Haze Rule
published on October 13, 2006, EPA
offered further clarification for states for
assessing alternative strategies, in
particular regarding the benchmark
definition of BART to use in judging
whether the alternative is better. 71 FR
60612. In this rulemaking, EPA stated in
the preamble that the presumptive
BART levels given in the BART
guidelines 1 would be a suitable baseline
against which to compare alternative
strategies, where the alternatives have
been designed to meet a requirement
other than BART. Id. at 60619; see also
40 CFR 51.308(e)(2)(i)(C). As described
in the EPA’s proposed approval of the
Illinois variance, EPA took a more
conservative approach and compared
emissions under the variance to the
application of typical BACT control
levels to the BART subject units in the
Ameren MPS Group.2 80 FR 21681,
21683 (April 20, 2015). In brief, EPA
found that the alternative restrictions
imposed by Illinois under the variance
can be demonstrated to provide greater
emission reductions and greater
visibility improvement than
conservative definitions of BART, even
without a full analysis of the emission
levels that constitute BART. The
demonstration is discussed below, in
the context of response to comments
addressing the magnitude of emission
reductions under the variance.
1 The BART guidelines are contained in
Appendix Y to 40 CFR part 51 and identify the
presumptive SO2 limits for utility boilers as 0.15
lbs/MMBtu or 95 percent control.
2 BACT limits are imposed on new units or units
undergoing major modifications. Therefore, BART
limits, which by definition apply to relatively old
existing units, are unlikely to be lower than the
limits that would apply to a new unit and would
in many cases be significantly higher. For this
analysis, a SO2 limit of 0.06 lbs/MMBtu was
determined to be representative of typical BACT for
utility boilers.
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Comment 2: The plain language of the
CAA ‘‘provides that EPA’s regulations
‘shall require’ each SIP to contain
various elements, and those elements
must include BART as a minimum
requirement of every haze SIP.’’ The
CAA does not permit a state to exempt
units from BART without going through
the exemption process outlined in the
statute. The statute specifies the only
circumstances in which a source may be
exempted from BART, none of which
apply here. 42 U.S.C. 7491(c). The CAA
provision that allows some limited
exemptions from BART makes plain
that any such exemption must be
assessed and determined on a sourcespecific, not a state-wide basis. Id. at
7491(c)(1). Furthermore, EPA may
exempt a unit from the source-specific
BART requirements of the CAA only
where the Federal Land Managers
concur with the EPA determination of
an exemption. Id. at 7491(c)(3).
Response 2: We do not agree that the
provisions governing exemptions to
BART apply. Neither the Illinois
Regional Haze SIP previously approved
by EPA nor the revisions to that SIP
contained in the variance being
approved in this action exempt BARTeligible sources from BART
requirements, but rather satisfy the
BART requirements through the
adoption of an alternative program that
provides greater reasonable progress
towards improving visibility.
Section 169A(b)(2) of the CAA, 42
U.S.C. 9491(b)(2), requires each
visibility SIP to contain ‘‘such emission
limits, schedules of compliance and
other measures as may be necessary to
make reasonable progress toward
meeting the national goal * * *
including * * * a requirement that
[certain major stationary sources] * * *
procure, install, and operate * * *
[BART].’’ Based on this language, EPA
concluded in the Regional Haze Rule
that if an alternative program can be
shown to make greater reasonable
progress toward eliminating or reducing
visibility impairment, then installing
BART for the purpose of making
reasonable progress toward the national
goal is no longer necessary. 64 FR
35714, 35739 (July 1, 1999).
This interpretation of the visibility
provisions of the CAA has been
previously challenged and upheld by
the D.C. Circuit. In the first case
challenging the provisions in the
Regional Haze Rule allowing for states
to adopt alternative programs in lieu of
BART, the court affirmed EPA’s
interpretation of CAA section
169A(b)(2) as allowing for alternatives
to BART where those alternatives will
result in greater reasonable progress
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79263
than BART. Center for Energy and
Economic Development v. EPA, 398
F.3d 653, 660 (D.C. Cir. 2005) (‘‘CEED’’)
(finding reasonable EPA’s interpretation
of CAA section 169(a)(2) as requiring
BART only as necessary to make
reasonable progress). In the second case,
Utility Air Regulatory Group v. EPA, 471
F.3d 1333 (D.C. Cir. 2006) (‘‘UARG’’),
the court specifically upheld EPA’s
determination that states could rely on
the Clean Air Interstate Rule (‘‘CAIR’’)
as an alternative program to BART for
EGUs in the CAIR-affected states. The
court concluded that the EPA’s twopronged test for determining whether an
alternative program achieves greater
reasonable progress was a reasonable
one and also agreed with EPA that
nothing in the CAA required the EPA to
‘‘impose a separate technology mandate
for sources whose emissions affect Class
I areas, rather than piggy-backing on
solutions devised under other statutory
categories, where such solutions meet
the statutory requirements.’’ Id. at 1340.
See also Central Arizona Water
Conservation District v. EPA, 990 F.2d
1531, 1543 (9th Cir. 1993) (upholding
EPA’s interpretation of CAA section
169A(b)(2)).
Comment 3: An interpretation of the
statute which allows a state to substitute
an alternative for BART on a state-wide
or fleet-wide basis cannot be reconciled
with Congress specifying very narrow
standards for exempting a source from
BART. If EPA relies on the D.C. Circuit
Court of Appeals decisions upholding
its interpretation of the statute, ‘‘the
cases are incorrect in that the D.C.
Circuit Court of Appeals has rewritten
the statute by failing to give effect to the
plain language requiring each SIP to
include BART and by disregarding the
very specific parameters in the statute
for exemptions from BART.’’ In
addition, ‘‘these decisions are not
binding precedent in the 7th Circuit,
which has jurisdiction over EPA’s
approval of the Illinois Regional Haze
SIP.’’
Response 3: EPA disagrees with the
commenter that BART alternatives are
impermissible under the CAA. As the
commenter notes, EPA’s interpretation
that the CAA allows States to devise
alternative programs in lieu of sourcespecific BART was upheld in both the
CEED and UARG decisions. The
conclusions in these cases have not
been upset or overturned by any
subsequent decision of the D.C. Circuit,
and we disagree with the commenter’s
contention that CEED and UARG were
decided erroneously. The D.C. Circuit
has exclusive jurisdiction over the
review of nationally applicable rules.
The Illinois’ SIP has been evaluated
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against nationally applicable rules
(upheld by the D.C. Circuit) that allow
States to adopt alternative measures in
lieu of BART.
Comment 4: The IEPA has not met its
burden to show that the Multi-Pollutant
Standard is approvable as a BART
alternative because it has not performed
modeling of the visibility impacts for
the MPS compared to BART. ‘‘By
design, the MPS allows the flexibility to
implement emissions reductions other
than by imposing uniform reductions at
specific units subject to BART.’’ There
is, therefore, no basis for claiming that
the distribution of emissions under the
MPS is not substantially different than
under BART. Instead, the MPS limits
can be met in such a way that the
distribution of emissions is significantly
different than it would be if its subjectto-BART units had to meet unit specific
BART limits. ‘‘If the distribution of
emissions is significantly different
under an alternate program, a state must
conduct visibility modeling in order to
meet its burden of securing approval for
the alternative program.’’
Response 4: EPA disagrees with the
commenter that visibility modeling is
required. EPA found in its original
approval of Illinois’ BART plan that the
distances from the relevant power
plants to the affected Class I areas are
substantial and that the averaging in
Illinois’ plan is only allowed within
somewhat limited regions. Given this,
EPA concluded that ‘‘a reallocation of
emission reductions from one plant to
another is unlikely to change the impact
of those emission reductions
significantly’’ and that the much greater
emission reductions from Illinois’ plan
will result in greater reasonable progress
than would source-specific BART
controls. 77 FR 39946. The commenter
has provided no evidence that EPA’s
conclusion that the greater reductions in
emissions from these facilities under the
terms of the variance should lead to a
different conclusion.
The commenter points to a test set out
in 40 CFR 51.308(e)(3) to support its
argument that visibility modeling is
necessary to determine whether an
alternative to BART provides for greater
reasonable progress. States are not
required to use this test, however, as 40
CFR 51.308(e)(2)(i)(E) makes clear: A
demonstration that an alternative
measure will make greater reasonable
progress may be based on the clear
weight of evidence. Although there is no
requirement that States use the test in
51.308(e)(3), EPA nevertheless
reexamined whether modeling is
necessary to conclude that the greater
emission reductions of Illinois’ revised
plan provide for better visibility than
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imposition of source-specific BART.
There are seven facilities in the Ameren
MPS Group: Coffeen Energy Center
(Montgomery County), Duck Creek
Energy Center (Fulton County), E.D.
Edwards Energy Center (Peoria County),
Joppa Energy Center (Massac County),
Newton Energy Center (Jasper County),
Meredosia Energy Center (Morgan
County) and Hutsonville Energy Center
(Crawford County). Of these facilities,
only Coffeen, Duck Creek, and E.D.
Edwards were determined to be subject
to BART. The least distance from any of
these three BART-subject sources to any
Class I area is from Coffeen to the Mingo
Wilderness Area, a distance of about
240 kilometers (km). Duck Creek and
E.D. Edwards are approximately 390 km
and 410 km, respectively, from the
Mingo Wilderness area. The distance
from the Mingo Wilderness Area to
remaining Ameren MPS Group facilities
ranges from approximately 120 km to
330 km, with an average distance of 260
km. Further, an evaluation for the Class
I areas within 500 km of any Ameren
MPS Group source shows that in every
case the average distance from the
BART-subject facilities is greater than
the average distance from the facilities
that would not be subject to BART. That
is, even if Illinois’ plan achieved no
more emission reductions than sourcespecific BART, the plan would likely
yield better visibility because the
reductions would likely be reallocated
to closer plants. Given these distances
and given the relative location of these
facilities, a reallocation of emission
reductions from one plant to another
among this group is unlikely to change
the visibility impact of these emission
reductions meaningfully. As noted
above, however, the Illinois plan
(originally and as revised) achieves
significantly greater reductions than
source-specific BART. Consequently, in
these circumstances, EPA is confident
that visibility modeling is not necessary
to conclude that the significantly greater
emission reductions that are required
under the variance will yield greater
progress toward visibility protection as
compared to the benefits of a
conservative estimate of BART.
Comment 5: The variance from the
MPS authorizes the IPH fleet to emit
greater SO2 emissions than would be
emitted if BART were required, and
thus EPA cannot find that the MPS will
lead to greater reasonable progress than
would BART.
Of the seven plants included in the
original Ameren MPS Group, five plants
still in operation are now owned and
operated by IPH and two plants that
retired in 2011, Hutsonville and
Meredosia, are now owned by Medina
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Valley and are no longer part of the
fleet. Because of the variance, the MPS
will no longer require SO2 reductions
from the IPH coal fleet during the period
of the first long-term strategy for
regional haze (i.e., before 2018) that are
greater than the reductions that would
result from requiring IPH to install and
operate BART on its BART-subject
plants.
The commenter supports this
assertion by comparing emissions
reductions from the variance to
emissions reductions from BACT at
BART-subject facilities, excluding
emissions reductions from the retired
Meredosia and Hutsonville units (now
owned by Medina Valley) and emissions
reductions from the Edwards Unit 1
(owned by IPH). The commenter states
that these sources were not included in
the analysis because Meredosia and
Hutsonville ‘‘have been retired for
several years due to economic reasons,’’
and Edwards Unit 1 is currently being
operated only for grid reliability
purposes subject to a short-term System
Support Resource agreement with the
Midcontinent Independent System
Operator (MISO). The commenter argues
that the MPS is not driving emissions
reductions at those sources and they
should not be included in any analysis
of emissions reductions at the IPH fleet.
The commenter’s analysis shows that, in
2017, implementation of BART at
BART-subject sources would reduce
SO2 emissions by 74,348 tons and the
variance would reduce SO2 by 69,555
tons.
Response 5: EPA disagrees with the
commenter’s assertion that EPA cannot
find that the MPS will lead to greater
reasonable progress than would BART.
The premise of the commenter’s
analysis, that only currently operating
units in the IPH fleet should be
evaluated, is flawed. As discussed
above, the requirement for BART may
be satisfied by an alternate program that
provides greater reasonable progress
toward visibility improvement than
direct application of BART to individual
sources determined to be subject to the
BART requirement. The alternate
program being evaluated, as contained
in the MPS and revised by the variance,
applies to the seven sources in the
Ameren MPS Group, not only to the five
sources currently owned and operated
by IPH.
The variance prohibits the Meredosia
and Hutsonville power stations from
operating until after December 31, 2020,
at which point they would remain
subject to the emission limits in the
MPS. In addition, the variance requires
IPH to permanently retire E.D. Edwards
Unit 1 as soon as allowed by MISO. The
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Federal Register / Vol. 80, No. 244 / Monday, December 21, 2015 / Rules and Regulations
fact that there are reasons other than the
MPS that influenced the decisions to
cease operation of these plants does not
change the fact that under the currently
approved Regional Haze SIP these
sources are permitted to operate. The
variance makes these shutdowns
enforceable and prohibits emissions that
would otherwise have been allowed
under the SIP. Further, these facilities
ceased operating late in 2011, well after
the 2000–2004 baseline established in
the Regional Haze Rule (40 CFR
51.308(d)(2)) and before the 2017
deadline for implementing BART
controls in Illinois, so the emission
reductions from the shutdown of these
facilities are fully creditable. Therefore,
comparing emission reductions at all
seven Ameren MPS Group sources
under the variance to emission
reductions from application of BACT
limits to BART-subject units is the
appropriate test for determining
whether the alternate program would
result in greater emission reductions.
The analysis included by EPA in the
proposed rule shows SO2 emission
reductions of 74,348 tons in 2017 if
typical BACT limits were applied to
BART subject sources and SO2 emission
reductions of 119,833 tons in 2017
under the variance. 80 FR 21683–21684.
The analysis is conservative in that it
assumes that E.D. Edwards Unit 1 is still
operating, since an absolute shutdown
date was not included in the variance.
Further, even assuming that the
22,360,000 MMBtu previously generated
at Meredosia and Hutsonville were
shifted to the five remaining facilities in
the Ameren MPS Group, applying the
0.35 pound/MMBtu group average
emission limit results in an additional
3,913 tons of SO2 emissions under the
variance in 2017, or a total of 54,188
tons of SO2. Thus, SO2 emissions
reductions in 2017 under the variance
would be 115,920 tons, which is still
41,572 fewer tons of SO2 emissions than
what the SO2 emissions would be if
BACT were applied at BART-subject
sources.
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III. Final Action
EPA is finalizing approval of the IPH
and Medina Valley variance submitted
by IEPA on September 3, 2014, as a
revision to the Illinois Regional Haze
SIP.
IV. Incorporation by Reference
In this rule, 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 the Illinois Regulations
described in the amendments to 40 CFR
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15:24 Dec 18, 2015
Jkt 238001
part 52 set forth below. EPA has made,
and will continue to make, these
documents generally available
electronically through
www.regulations.gov and/or in hard
copy at the appropriate EPA office (see
the ADDRESSES section of this preamble
for more information).
V. Statutory and Executive Order
Reviews
Under the CAA, the Administrator is
required to approve a SIP submission
that complies with the provisions of the
CAA and applicable Federal regulations.
42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions,
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this action
merely approves state law as meeting
Federal requirements and does not
impose additional requirements beyond
those imposed by state law. For that
reason, this action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
of Management and Budget under
Executive Orders 12866 (58 FR 51735,
October 4, 1993) and 13563 (76 FR 3821,
January 21, 2011);
• Does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• Is certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.);
• Does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
• Does not have Federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• Is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
• Is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• Is not subject to requirements of
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
application of those requirements would
be inconsistent with the CAA; and
• Does not provide EPA with the
discretionary authority to address, as
appropriate, disproportionate human
health or environmental effects, using
practicable and legally permissible
methods, under Executive Order 12898
(59 FR 7629, February 16, 1994).
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Fmt 4700
Sfmt 4700
79265
In addition, the SIP is not approved
to apply on any Indian reservation land
or in any other area where EPA or an
Indian tribe has demonstrated that a
tribe has jurisdiction. In those areas of
Indian country, the rule does not have
tribal implications and will not impose
substantial direct costs on tribal
governments or preempt tribal law as
specified by Executive Order 13175 (65
FR 67249, November 9, 2000).
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).
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 February 19, 2016. 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 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, Intergovernmental relations,
Particulate matter, Reporting and
recordkeeping requirements, Sulfur
oxides.
Dated: November 24, 2015.
Susan Hedman,
Regional Administrator, Region 5.
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.
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Federal Register / Vol. 80, No. 244 / Monday, December 21, 2015 / Rules and Regulations
2. Section 52.720 is amended by
adding paragraph (c)(207) to read as
follows:
■
§ 52.720
Identification of plan.
*
*
*
*
*
(c) * * *
(207) On September 3, 2014, Illinois
submitted a variance to its regional haze
state implementation plan affecting the
electrical generating units (EGUs)
included in the Ameren Multi-Pollutant
Standard Group (Ameren MPS Group).
The Ameren MPS Group consists of five
facilities owned by Illinois Power
Holdings, LLC (IPH) and two facilities
owned by AmerenEnergy Medina Valley
Cogen, LLC (Medina Valley). The IPH
facilities included in the Ameren MPS
Group and subject to the variance
include: Coffeen Energy Center
(Montgomery County), Duck Creek
Energy Center (Fulton County), E.D.
Edwards Energy Center (Peoria County),
Joppa Energy Center (Massac County),
and Newton Energy Center (Jasper
County). The Medina Valley facilities
included in the Ameren MPS Group and
subject to the variance are the
Meredosia Energy Center (Morgan
County) and the Hutsonville Energy
Center (Crawford County).
(i) Incorporation by reference.
(A) Illinois Pollution Control Board
Order PCB 14–10, adopted on November
21, 2013; Certificate of Acceptance, filed
with the Illinois Pollution Control Board
Clerk’s Office December 20, 2013.
[FR Doc. 2015–31882 Filed 12–21–15; 8:45 am]
BILLING CODE 6560–50–P
emissions that will contribute
significantly to nonattainment or
interfere with maintenance of the 2008
ozone National Ambient Air Quality
Standard (NAAQS) in any other state.
This final rule is effective
January 20, 2016.
DATES:
The EPA has established a
docket for this action under Docket ID
No. EPA–R10–OAR–2015–0259. All
documents in the docket are listed on
the https://www.regulations.gov Web
site. Although listed in the index, some
information is not publicly available,
e.g., Confidential Business Information
(CBI) or other information the disclosure
of which is restricted by statute. Certain
other material, such as copyrighted
material, is not placed on the Internet
and will be publicly available only in
hard copy form. Publicly available
docket materials are available either
electronically through https://
www.regulations.gov or in hard copy at
the Air Programs Unit, Office of Air,
Waste and Toxics, EPA Region 10, 1200
Sixth Avenue, Seattle, WA, 98101. The
EPA requests that if at all possible, you
contact the individual listed in the FOR
FURTHER INFORMATION CONTACT section to
view the hard copy of the docket. You
may view the hard copy of the docket
Monday through Friday, 8:00 a.m. to
4:00 p.m., excluding Federal holidays.
ADDRESSES:
FOR FURTHER INFORMATION CONTACT:
Kristin Hall at (206) 553–6357,
hall.kristin@epa.gov, or the above EPA,
Region 10 address.
SUPPLEMENTARY INFORMATION:
Table of Contents
ENVIRONMENTAL PROTECTION
AGENCY
I. Background Information
II. Final Action
III. Statutory and Executive Orders Review
40 CFR Part 52
[EPA–R10–OAR–2015–0259; FRL–9940–35–
Region 10]
I. Background Information
Environmental Protection
Agency.
ACTION: Final rule.
The Clean Air Act (CAA)
requires each State Implementation Plan
(SIP) to contain adequate provisions
prohibiting air emissions that will have
certain adverse air quality effects in
other states. On June 28, 2010, the State
of Oregon made a submittal to the
Environmental Protection Agency (EPA)
to address these requirements. The EPA
is approving the submittal as meeting
the requirement that each SIP contain
adequate provisions to prohibit
On October 27, 2015, the EPA
proposed to approve Oregon’s June 28,
2010 submittal as meeting the interstate
transport requirements of CAA section
110(a)(2)(D)(i)(I) for the 2008 ozone
NAAQS (80 FR 65680). An explanation
of the CAA requirements, a detailed
analysis of the submittal, and the EPA’s
reasons for approval were provided in
the notice of proposed rulemaking, and
will not be restated here. The public
comment period for this proposed rule
ended on November 27, 2015. The EPA
received no comments on the proposal.
II. Final Action
Approval and Promulgation of
Implementation Plans; Oregon:
Interstate Transport of Ozone
AGENCY:
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SUMMARY:
VerDate Sep<11>2014
15:24 Dec 18, 2015
Jkt 238001
The EPA is approving Oregon’s June
28, 2010 submittal as meeting the CAA
section 110(a)(2)(D)(i)(I) interstate
transport requirements for the 2008
ozone NAAQS.
PO 00000
Frm 00036
Fmt 4700
Sfmt 4700
III. Statutory and Executive Orders
Review
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, the
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this action
merely approves state law as meeting
Federal requirements and does not
impose additional requirements beyond
those imposed by state law. For that
reason, this action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
of Management and Budget under
Executive Orders 12866 (58 FR 51735,
October 4, 1993) and 13563 (76 FR 3821,
January 21, 2011);
• Does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• Is certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.);
• Does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
• Does not have Federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• Is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
• Is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• Is not subject to requirements of
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
this action does not involve technical
standards; and
• Does not provide the 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, the SIP is not approved
to apply on any Indian reservation land
or in any other area where the EPA or
an Indian tribe has demonstrated that a
tribe has jurisdiction. In those areas of
Indian country, the rule does not have
tribal implications as specified by
Executive Order 13175 (65 FR 67249,
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Agencies
[Federal Register Volume 80, Number 244 (Monday, December 21, 2015)]
[Rules and Regulations]
[Pages 79261-79266]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2015-31882]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R05-OAR-2014-0705; FRL-9939-75-Region 5]
Air Quality Implementation Plan Approval; Illinois; Illinois
Power Holdings and AmerenEnergy Medina Valley Cogen Variance
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) is approving into
the Illinois Regional Haze State Implementation Plan (SIP) a variance
for the electrical generating units (EGUs) included in the Ameren
Multi-Pollutant Standard Group (Ameren MPS Group). The Ameren MPS Group
consists of five facilities owned by Illinois Power Holdings, LLC (IPH)
and two facilities owned by AmerenEnergy Medina Valley Cogen, LLC
(Medina Valley). The Illinois Environmental Protection Agency (IEPA)
submitted the variance to EPA for approval on September 3, 2014.
[[Page 79262]]
DATES: This final rule is effective on January 20, 2016.
ADDRESSES: EPA has established a docket for this action under Docket ID
No. EPA-R05-OAR-2014-0705. All documents in the docket are listed on
the www.regulations.gov Web site. Although listed in the index, 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 at the
Environmental Protection Agency, Region 5, Air and Radiation Division,
77 West Jackson Boulevard, Chicago, Illinois 60604. This facility is
open from 8:30 a.m. to 4:30 p.m., Monday through Friday, excluding
Federal holidays. We recommend that you telephone Kathleen D'Agostino,
Environmental Engineer, at (312) 886-1767 before visiting the Region 5
office.
FOR FURTHER INFORMATION CONTACT: Kathleen D'Agostino, Environmental
Engineer, Attainment Planning and Maintenance Section, Air Programs
Branch (AR-18J), Environmental Protection Agency, Region 5, 77 West
Jackson Boulevard, Chicago, Illinois 60604, (312) 886-1767,
dagostino.kathleen@epa.gov.
SUPPLEMENTARY INFORMATION: Throughout this document whenever ``we,''
``us,'' or ``our'' is used, we mean EPA. This supplementary information
section is arranged as follows:
I. Background
II. Response to Comments
III. Final Action
IV. Incorporation by Reference
V. Statutory and Executive Order Reviews
I. Background
On June 24, 2011, Illinois submitted a plan to address the
requirements of the Regional Haze Rule, as codified at 40 CFR 51.308.
EPA approved Illinois' Regional Haze SIP on July 6, 2012 (77 FR 39943).
In its approval, EPA determined that the emission reductions from
sources included in the Illinois plan are significantly greater than
even conservative definitions of best available retrofit technology
(BART) applied to BART subject units. Id. at 39946. EPA also addressed
whether the Illinois plan can also be expected to achieve greater
visibility protection than application of BART on BART-subject units.
Given that, in general, the Illinois power plants are substantial
distances from any Class I area, and given that the averaging in
Illinois' plan is only authorized within the somewhat limited region
within which each utility's plants are located, EPA determined that a
reallocation of emission reductions from one plant to another is
unlikely to change the visibility impact of those emission reductions
significantly. Consequently, EPA concluded that the significantly
greater emission reductions that Illinois required in its Regional Haze
SIP will yield greater progress toward visibility protection as
compared to the benefits of a conservative estimate of BART.
One of the rules approved in that action to meet BART requirements
is 35 Illinois Administrative Code (Ill. Adm. Code) rule 225.233,
Multi-Pollutant Standard (MPS), specifically subsections (a), (b), (e),
and (g). Section 225.233(e)(3)(C) contains the sulfur dioxide
(SO2) emission standards applicable to the Ameren MPS Group.
Section 225.233(e)(3)(C)(i) establishes an overall SO2
annual emission rate for EGUs in the Ameren MPS group of 0.50 pounds
per million Btu (lb/mmBtu) for calendar years 2010 through 2013.
Section 225.233(e)(3)(C)(ii) establishes an overall SO2
annual emission rate for EGUs in the Ameren MPS group of 0.43 lb/mmBtu
for calendar year 2014. Section 225.233(e)(3)(C)(iii) establishes an
overall SO2 annual emission rate for EGUs in the Ameren MPS
group of 0.25 lb/mmBtu for calendar years 2015 and 2016. Section
225.233(e)(3)(C)(iv) establishes an overall SO2 annual
emission rate for EGUs in the Ameren MPS group of 0.23 lb/mmBtu
beginning in calendar year 2017 and continuing each calendar year
thereafter.
On November 21, 2013, the Illinois Pollution Control Board (IPCB)
granted IPH and Medina Valley a variance from the applicable
requirements of Section 225.233(e)(3)(C)(iii) for a period beginning
January 1, 2015, through December 31, 2019, and Section
225.233(e)(3)(C)(iv) for a period beginning January 1, 2017, through
December 31, 2019, subject to certain conditions. The IPH facilities
included in the Ameren MPS Group and subject to the variance are
Coffeen Energy Center (Montgomery County), Duck Creek Energy Center
(Fulton County), E.D. Edwards Energy Center (Peoria County), Joppa
Energy Center (Massac County), and Newton Energy Center (Jasper
County). The Medina Valley facilities included in the Ameren MPS Group
and subject to the variance are the Meredosia Energy Center (Morgan
County) and the Hutsonville Energy Center (Crawford County). IEPA
submitted the variance as a revision to the Illinois Regional Haze SIP
on September 3, 2014.
EPA proposed to approve the variance on April 20, 2015 (80 FR
21681). As discussed in the proposal, the variance results in less
SO2 emissions than the currently approved Regional Haze SIP.
Id. at 21683. In addition, EPA determined that the significantly lower
SO2 emissions under the variance versus application of Best
Available Control Technology (BACT) to BART-subject sources, will yield
greater progress toward visibility protection. Id. at 21684. Finally,
with respect to the requirements of section 110(l) of the Clean Air Act
(CAA) (42 U.S.C. 7410(l)), because the variance will result in less
SO2 emissions than the currently approved Regional Haze SIP
and will continue to provide better visibility protection than the
application of BART to BART-subject units, EPA has determined that the
variance will not interfere with attainment, reasonable further
progress, or any other applicable requirement of the CAA. Id. at 21684.
II. Response to Comments
EPA received joint adverse comments from Earthjustice and Sierra
Club, as summarized in the comments/responses below.
Comment 1: The proposed SIP revision unlawfully substitutes fleet-
wide emission limits for the unit-specific five factor BART analysis
required by the CAA.
Response 1: Section 169A(b)(2)(A) of the CAA, 42 U.S.C.
7491(b)(2)(A), requires states to revise their SIPs to contain such
measures as may be necessary to make reasonable progress towards the
natural visibility goal, including a requirement that certain existing
major stationary sources procure, install, and operate BART, as
determined by the state. In some cases, this requirement is met with an
analysis of potential controls for each source subject to BART
considering five factors set out in EPA's regional haze rule. 40 CFR
51.308(e)(1)(ii)(A). However, as described in several previous rules,
EPA has concluded that CAA section 169A may reasonably be interpreted
to provide that the requirement for BART may be satisfied by an
alternate program that provides greater reasonable progress toward
visibility improvement than direct application of BART to individual
sources determined to be subject to the BART requirement. See 40 CFR
51.308(e), 64 FR 35714, 35741-35743 (July 1, 1999), 70 FR 39104, 39136
(July 6, 2005), 71 FR 60612 (October 13, 2006), and 77 FR 33642 (June
7, 2012).
[[Page 79263]]
In 1999, EPA promulgated the Regional Haze Rule, which established
a comprehensive visibility protection program for mandatory Class I
Federal areas (including many national parks and wilderness areas). In
the preamble to the Regional Haze Rule, EPA stated that, to demonstrate
that emission reductions of an alternative program would result in
greater emission reductions, ``the State must estimate the emission
reductions that would result from the use of BART-level controls. To do
this, the State could undertake a source-specific review of the sources
in the State subject to BART, or it could use a modified approach that
simplifies the analysis.'' 64 FR 35742 (July 1, 1999).
In a final rule revising certain provisions of the Regional Haze
Rule published on October 13, 2006, EPA offered further clarification
for states for assessing alternative strategies, in particular
regarding the benchmark definition of BART to use in judging whether
the alternative is better. 71 FR 60612. In this rulemaking, EPA stated
in the preamble that the presumptive BART levels given in the BART
guidelines \1\ would be a suitable baseline against which to compare
alternative strategies, where the alternatives have been designed to
meet a requirement other than BART. Id. at 60619; see also 40 CFR
51.308(e)(2)(i)(C). As described in the EPA's proposed approval of the
Illinois variance, EPA took a more conservative approach and compared
emissions under the variance to the application of typical BACT control
levels to the BART subject units in the Ameren MPS Group.\2\ 80 FR
21681, 21683 (April 20, 2015). In brief, EPA found that the alternative
restrictions imposed by Illinois under the variance can be demonstrated
to provide greater emission reductions and greater visibility
improvement than conservative definitions of BART, even without a full
analysis of the emission levels that constitute BART. The demonstration
is discussed below, in the context of response to comments addressing
the magnitude of emission reductions under the variance.
---------------------------------------------------------------------------
\1\ The BART guidelines are contained in Appendix Y to 40 CFR
part 51 and identify the presumptive SO2 limits for
utility boilers as 0.15 lbs/MMBtu or 95 percent control.
\2\ BACT limits are imposed on new units or units undergoing
major modifications. Therefore, BART limits, which by definition
apply to relatively old existing units, are unlikely to be lower
than the limits that would apply to a new unit and would in many
cases be significantly higher. For this analysis, a SO2
limit of 0.06 lbs/MMBtu was determined to be representative of
typical BACT for utility boilers.
---------------------------------------------------------------------------
Comment 2: The plain language of the CAA ``provides that EPA's
regulations `shall require' each SIP to contain various elements, and
those elements must include BART as a minimum requirement of every haze
SIP.'' The CAA does not permit a state to exempt units from BART
without going through the exemption process outlined in the statute.
The statute specifies the only circumstances in which a source may be
exempted from BART, none of which apply here. 42 U.S.C. 7491(c). The
CAA provision that allows some limited exemptions from BART makes plain
that any such exemption must be assessed and determined on a source-
specific, not a state-wide basis. Id. at 7491(c)(1). Furthermore, EPA
may exempt a unit from the source-specific BART requirements of the CAA
only where the Federal Land Managers concur with the EPA determination
of an exemption. Id. at 7491(c)(3).
Response 2: We do not agree that the provisions governing
exemptions to BART apply. Neither the Illinois Regional Haze SIP
previously approved by EPA nor the revisions to that SIP contained in
the variance being approved in this action exempt BART-eligible sources
from BART requirements, but rather satisfy the BART requirements
through the adoption of an alternative program that provides greater
reasonable progress towards improving visibility.
Section 169A(b)(2) of the CAA, 42 U.S.C. 9491(b)(2), requires each
visibility SIP to contain ``such emission limits, schedules of
compliance and other measures as may be necessary to make reasonable
progress toward meeting the national goal * * * including * * * a
requirement that [certain major stationary sources] * * * procure,
install, and operate * * * [BART].'' Based on this language, EPA
concluded in the Regional Haze Rule that if an alternative program can
be shown to make greater reasonable progress toward eliminating or
reducing visibility impairment, then installing BART for the purpose of
making reasonable progress toward the national goal is no longer
necessary. 64 FR 35714, 35739 (July 1, 1999).
This interpretation of the visibility provisions of the CAA has
been previously challenged and upheld by the D.C. Circuit. In the first
case challenging the provisions in the Regional Haze Rule allowing for
states to adopt alternative programs in lieu of BART, the court
affirmed EPA's interpretation of CAA section 169A(b)(2) as allowing for
alternatives to BART where those alternatives will result in greater
reasonable progress than BART. Center for Energy and Economic
Development v. EPA, 398 F.3d 653, 660 (D.C. Cir. 2005) (``CEED'')
(finding reasonable EPA's interpretation of CAA section 169(a)(2) as
requiring BART only as necessary to make reasonable progress). In the
second case, Utility Air Regulatory Group v. EPA, 471 F.3d 1333 (D.C.
Cir. 2006) (``UARG''), the court specifically upheld EPA's
determination that states could rely on the Clean Air Interstate Rule
(``CAIR'') as an alternative program to BART for EGUs in the CAIR-
affected states. The court concluded that the EPA's two-pronged test
for determining whether an alternative program achieves greater
reasonable progress was a reasonable one and also agreed with EPA that
nothing in the CAA required the EPA to ``impose a separate technology
mandate for sources whose emissions affect Class I areas, rather than
piggy-backing on solutions devised under other statutory categories,
where such solutions meet the statutory requirements.'' Id. at 1340.
See also Central Arizona Water Conservation District v. EPA, 990 F.2d
1531, 1543 (9th Cir. 1993) (upholding EPA's interpretation of CAA
section 169A(b)(2)).
Comment 3: An interpretation of the statute which allows a state to
substitute an alternative for BART on a state-wide or fleet-wide basis
cannot be reconciled with Congress specifying very narrow standards for
exempting a source from BART. If EPA relies on the D.C. Circuit Court
of Appeals decisions upholding its interpretation of the statute, ``the
cases are incorrect in that the D.C. Circuit Court of Appeals has
rewritten the statute by failing to give effect to the plain language
requiring each SIP to include BART and by disregarding the very
specific parameters in the statute for exemptions from BART.'' In
addition, ``these decisions are not binding precedent in the 7th
Circuit, which has jurisdiction over EPA's approval of the Illinois
Regional Haze SIP.''
Response 3: EPA disagrees with the commenter that BART alternatives
are impermissible under the CAA. As the commenter notes, EPA's
interpretation that the CAA allows States to devise alternative
programs in lieu of source-specific BART was upheld in both the CEED
and UARG decisions. The conclusions in these cases have not been upset
or overturned by any subsequent decision of the D.C. Circuit, and we
disagree with the commenter's contention that CEED and UARG were
decided erroneously. The D.C. Circuit has exclusive jurisdiction over
the review of nationally applicable rules. The Illinois' SIP has been
evaluated
[[Page 79264]]
against nationally applicable rules (upheld by the D.C. Circuit) that
allow States to adopt alternative measures in lieu of BART.
Comment 4: The IEPA has not met its burden to show that the Multi-
Pollutant Standard is approvable as a BART alternative because it has
not performed modeling of the visibility impacts for the MPS compared
to BART. ``By design, the MPS allows the flexibility to implement
emissions reductions other than by imposing uniform reductions at
specific units subject to BART.'' There is, therefore, no basis for
claiming that the distribution of emissions under the MPS is not
substantially different than under BART. Instead, the MPS limits can be
met in such a way that the distribution of emissions is significantly
different than it would be if its subject-to-BART units had to meet
unit specific BART limits. ``If the distribution of emissions is
significantly different under an alternate program, a state must
conduct visibility modeling in order to meet its burden of securing
approval for the alternative program.''
Response 4: EPA disagrees with the commenter that visibility
modeling is required. EPA found in its original approval of Illinois'
BART plan that the distances from the relevant power plants to the
affected Class I areas are substantial and that the averaging in
Illinois' plan is only allowed within somewhat limited regions. Given
this, EPA concluded that ``a reallocation of emission reductions from
one plant to another is unlikely to change the impact of those emission
reductions significantly'' and that the much greater emission
reductions from Illinois' plan will result in greater reasonable
progress than would source-specific BART controls. 77 FR 39946. The
commenter has provided no evidence that EPA's conclusion that the
greater reductions in emissions from these facilities under the terms
of the variance should lead to a different conclusion.
The commenter points to a test set out in 40 CFR 51.308(e)(3) to
support its argument that visibility modeling is necessary to determine
whether an alternative to BART provides for greater reasonable
progress. States are not required to use this test, however, as 40 CFR
51.308(e)(2)(i)(E) makes clear: A demonstration that an alternative
measure will make greater reasonable progress may be based on the clear
weight of evidence. Although there is no requirement that States use
the test in 51.308(e)(3), EPA nevertheless reexamined whether modeling
is necessary to conclude that the greater emission reductions of
Illinois' revised plan provide for better visibility than imposition of
source-specific BART. There are seven facilities in the Ameren MPS
Group: Coffeen Energy Center (Montgomery County), Duck Creek Energy
Center (Fulton County), E.D. Edwards Energy Center (Peoria County),
Joppa Energy Center (Massac County), Newton Energy Center (Jasper
County), Meredosia Energy Center (Morgan County) and Hutsonville Energy
Center (Crawford County). Of these facilities, only Coffeen, Duck
Creek, and E.D. Edwards were determined to be subject to BART. The
least distance from any of these three BART-subject sources to any
Class I area is from Coffeen to the Mingo Wilderness Area, a distance
of about 240 kilometers (km). Duck Creek and E.D. Edwards are
approximately 390 km and 410 km, respectively, from the Mingo
Wilderness area. The distance from the Mingo Wilderness Area to
remaining Ameren MPS Group facilities ranges from approximately 120 km
to 330 km, with an average distance of 260 km. Further, an evaluation
for the Class I areas within 500 km of any Ameren MPS Group source
shows that in every case the average distance from the BART-subject
facilities is greater than the average distance from the facilities
that would not be subject to BART. That is, even if Illinois' plan
achieved no more emission reductions than source-specific BART, the
plan would likely yield better visibility because the reductions would
likely be reallocated to closer plants. Given these distances and given
the relative location of these facilities, a reallocation of emission
reductions from one plant to another among this group is unlikely to
change the visibility impact of these emission reductions meaningfully.
As noted above, however, the Illinois plan (originally and as revised)
achieves significantly greater reductions than source-specific BART.
Consequently, in these circumstances, EPA is confident that visibility
modeling is not necessary to conclude that the significantly greater
emission reductions that are required under the variance will yield
greater progress toward visibility protection as compared to the
benefits of a conservative estimate of BART.
Comment 5: The variance from the MPS authorizes the IPH fleet to
emit greater SO2 emissions than would be emitted if BART
were required, and thus EPA cannot find that the MPS will lead to
greater reasonable progress than would BART.
Of the seven plants included in the original Ameren MPS Group, five
plants still in operation are now owned and operated by IPH and two
plants that retired in 2011, Hutsonville and Meredosia, are now owned
by Medina Valley and are no longer part of the fleet. Because of the
variance, the MPS will no longer require SO2 reductions from
the IPH coal fleet during the period of the first long-term strategy
for regional haze (i.e., before 2018) that are greater than the
reductions that would result from requiring IPH to install and operate
BART on its BART-subject plants.
The commenter supports this assertion by comparing emissions
reductions from the variance to emissions reductions from BACT at BART-
subject facilities, excluding emissions reductions from the retired
Meredosia and Hutsonville units (now owned by Medina Valley) and
emissions reductions from the Edwards Unit 1 (owned by IPH). The
commenter states that these sources were not included in the analysis
because Meredosia and Hutsonville ``have been retired for several years
due to economic reasons,'' and Edwards Unit 1 is currently being
operated only for grid reliability purposes subject to a short-term
System Support Resource agreement with the Midcontinent Independent
System Operator (MISO). The commenter argues that the MPS is not
driving emissions reductions at those sources and they should not be
included in any analysis of emissions reductions at the IPH fleet. The
commenter's analysis shows that, in 2017, implementation of BART at
BART-subject sources would reduce SO2 emissions by 74,348
tons and the variance would reduce SO2 by 69,555 tons.
Response 5: EPA disagrees with the commenter's assertion that EPA
cannot find that the MPS will lead to greater reasonable progress than
would BART. The premise of the commenter's analysis, that only
currently operating units in the IPH fleet should be evaluated, is
flawed. As discussed above, the requirement for BART may be satisfied
by an alternate program that provides greater reasonable progress
toward visibility improvement than direct application of BART to
individual sources determined to be subject to the BART requirement.
The alternate program being evaluated, as contained in the MPS and
revised by the variance, applies to the seven sources in the Ameren MPS
Group, not only to the five sources currently owned and operated by
IPH.
The variance prohibits the Meredosia and Hutsonville power stations
from operating until after December 31, 2020, at which point they would
remain subject to the emission limits in the MPS. In addition, the
variance requires IPH to permanently retire E.D. Edwards Unit 1 as soon
as allowed by MISO. The
[[Page 79265]]
fact that there are reasons other than the MPS that influenced the
decisions to cease operation of these plants does not change the fact
that under the currently approved Regional Haze SIP these sources are
permitted to operate. The variance makes these shutdowns enforceable
and prohibits emissions that would otherwise have been allowed under
the SIP. Further, these facilities ceased operating late in 2011, well
after the 2000-2004 baseline established in the Regional Haze Rule (40
CFR 51.308(d)(2)) and before the 2017 deadline for implementing BART
controls in Illinois, so the emission reductions from the shutdown of
these facilities are fully creditable. Therefore, comparing emission
reductions at all seven Ameren MPS Group sources under the variance to
emission reductions from application of BACT limits to BART-subject
units is the appropriate test for determining whether the alternate
program would result in greater emission reductions.
The analysis included by EPA in the proposed rule shows
SO2 emission reductions of 74,348 tons in 2017 if typical
BACT limits were applied to BART subject sources and SO2
emission reductions of 119,833 tons in 2017 under the variance. 80 FR
21683-21684. The analysis is conservative in that it assumes that E.D.
Edwards Unit 1 is still operating, since an absolute shutdown date was
not included in the variance. Further, even assuming that the
22,360,000 MMBtu previously generated at Meredosia and Hutsonville were
shifted to the five remaining facilities in the Ameren MPS Group,
applying the 0.35 pound/MMBtu group average emission limit results in
an additional 3,913 tons of SO2 emissions under the variance
in 2017, or a total of 54,188 tons of SO2. Thus,
SO2 emissions reductions in 2017 under the variance would be
115,920 tons, which is still 41,572 fewer tons of SO2
emissions than what the SO2 emissions would be if BACT were
applied at BART-subject sources.
III. Final Action
EPA is finalizing approval of the IPH and Medina Valley variance
submitted by IEPA on September 3, 2014, as a revision to the Illinois
Regional Haze SIP.
IV. Incorporation by Reference
In this rule, 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 the Illinois
Regulations described in the amendments to 40 CFR part 52 set forth
below. EPA has made, and will continue to make, these documents
generally available electronically through www.regulations.gov and/or
in hard copy at the appropriate EPA office (see the ADDRESSES section
of this preamble for more information).
V. Statutory and Executive Order Reviews
Under the CAA, the Administrator is required to approve a SIP
submission that complies with the provisions of the CAA and applicable
Federal regulations. 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in
reviewing SIP submissions, EPA's role is to approve state choices,
provided that they meet the criteria of the CAA. Accordingly, this
action merely approves state law as meeting Federal requirements and
does not impose additional requirements beyond those imposed by state
law. For that reason, this action:
Is not a ``significant regulatory action'' subject to
review by the Office of Management and Budget under Executive Orders
12866 (58 FR 51735, October 4, 1993) and 13563 (76 FR 3821, January 21,
2011);
Does not impose an information collection burden under the
provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et seq.);
Is certified as not having a significant economic impact
on a substantial number of small entities under the Regulatory
Flexibility Act (5 U.S.C. 601 et seq.);
Does not contain any unfunded mandate or significantly or
uniquely affect small governments, as described in the Unfunded
Mandates Reform Act of 1995 (Pub. L. 104-4);
Does not have Federalism implications as specified in
Executive Order 13132 (64 FR 43255, August 10, 1999);
Is not an economically significant regulatory action based
on health or safety risks subject to Executive Order 13045 (62 FR
19885, April 23, 1997);
Is not a significant regulatory action subject to
Executive Order 13211 (66 FR 28355, May 22, 2001);
Is not subject to requirements of Section 12(d) of the
National Technology Transfer and Advancement Act of 1995 (15 U.S.C. 272
note) because application of those requirements would be inconsistent
with the CAA; and
Does not provide EPA with the discretionary authority to
address, as appropriate, disproportionate human health or environmental
effects, using practicable and legally permissible methods, under
Executive Order 12898 (59 FR 7629, February 16, 1994).
In addition, the SIP is not approved to apply on any Indian
reservation land or in any other area where EPA or an Indian tribe has
demonstrated that a tribe has jurisdiction. In those areas of Indian
country, the rule does not have tribal implications and will not impose
substantial direct costs on tribal governments or preempt tribal law as
specified by Executive Order 13175 (65 FR 67249, November 9, 2000).
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).
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 February 19, 2016. 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 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, Intergovernmental relations, Particulate matter, Reporting
and recordkeeping requirements, Sulfur oxides.
Dated: November 24, 2015.
Susan Hedman,
Regional Administrator, Region 5.
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.
[[Page 79266]]
0
2. Section 52.720 is amended by adding paragraph (c)(207) to read as
follows:
Sec. 52.720 Identification of plan.
* * * * *
(c) * * *
(207) On September 3, 2014, Illinois submitted a variance to its
regional haze state implementation plan affecting the electrical
generating units (EGUs) included in the Ameren Multi-Pollutant Standard
Group (Ameren MPS Group). The Ameren MPS Group consists of five
facilities owned by Illinois Power Holdings, LLC (IPH) and two
facilities owned by AmerenEnergy Medina Valley Cogen, LLC (Medina
Valley). The IPH facilities included in the Ameren MPS Group and
subject to the variance include: Coffeen Energy Center (Montgomery
County), Duck Creek Energy Center (Fulton County), E.D. Edwards Energy
Center (Peoria County), Joppa Energy Center (Massac County), and Newton
Energy Center (Jasper County). The Medina Valley facilities included in
the Ameren MPS Group and subject to the variance are the Meredosia
Energy Center (Morgan County) and the Hutsonville Energy Center
(Crawford County).
(i) Incorporation by reference.
(A) Illinois Pollution Control Board Order PCB 14-10, adopted on
November 21, 2013; Certificate of Acceptance, filed with the Illinois
Pollution Control Board Clerk's Office December 20, 2013.
[FR Doc. 2015-31882 Filed 12-21-15; 8:45 am]
BILLING CODE 6560-50-P