Approval and Promulgation of Air Quality Implementation Plans; State of Nevada; Regional Haze State Implementation Plan, 17334-17341 [2012-7025]
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Chairman. In the event of the Vice
Chairman’s death, departure or
resignation prior to the election of a
successor, the Board, as soon as
practicable, shall elect a new Vice
Chairman who shall serve a term that
commences immediately upon election
and expires upon the election and
installation of a successor Vice
Chairman.
PART 6—MEETINGS (ARTICLE VI)
the next regularly scheduled Board
meeting following the date of the veto,
or to schedule a teleconference to
consider the matter, as appropriate.
(d) Disclosure of result. The Secretary
shall maintain all records pertaining to
Board actions taken pursuant to the
notation voting process, and shall make
such records available for public
inspection, consistent with the Freedom
of Information Act, 5 U.S.C. 552.
40 CFR Part 52
Available Retrofit Technology (BART) to
reduce nitrogen oxide (NOX) emissions
at the Reid Gardner Generating Station
(RGGS). We will take action on BART
for NOX at RGGS in a future notice.
DATES: Effective Date: This rule is
effective on April 25, 2012.
ADDRESSES: EPA has established docket
number EPA–R09–OAR–2011–0130 for
this action. Generally, documents in the
docket are available electronically at
https://www.regulations.gov or in hard
copy at EPA Region 9, 75 Hawthorne
Street, San Francisco, California. Please
note that while many of the documents
in the docket are listed at https://
www.regulations.gov, some information
may not be specifically listed in the
index to the docket and may be publicly
available only at the hard copy location
(e.g., copyrighted material, large maps,
multi-volume reports or otherwise
voluminous materials), and some may
not be available at either locations (e.g.,
confidential business information). To
inspect the hard copy materials, please
schedule an appointment during normal
business hours with the contact listed
directly below.
FOR FURTHER INFORMATION CONTACT:
Thomas Webb, U.S. EPA, Region 9,
Planning Office, Air Division, Air-2, 75
Hawthorne Street, San Francisco, CA
94105. Thomas Webb can be reached at
telephone number (415) 947–4139 and
via electronic mail at
webb.thomas@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document, wherever
‘‘we,’’ ‘‘us,’’ or ‘‘our,’’ is used, we mean
the United States Environmental
Protection Agency (EPA).
[EPA–R09–OAR–2011–0130, FRL–9612–7]
Table of Contents
Approval and Promulgation of Air
Quality Implementation Plans; State of
Nevada; Regional Haze State
Implementation Plan
I. Background
A. Description of Regional Haze
B. History of Regional Haze Regulations
C. Our Proposed Action
II. BART Determination for NOX at Reid
Gardner
A. Background
B. NDEP’s Determination
C. Public Comments Relevant to NDEP’s
Determination
D. EPA’s Analysis
III. EPA Responses to Public Comments
Except BART for NOX at RGGS
A. Reasonable Progress Goal
B. Long-Term Strategy
C. BART for SO2 and PM10 at Reid Gardner
D. Corrections to EPA’s Technical Analysis
IV. EPA Action
V. Statutory and Executive Order Reviews
PART 7—PUBLIC OBSERVATION
(ARTICLE VII)
4. The authority citation for part 6
continues to read as follows:
■
Authority: 39 U.S.C. 202, 205, 401(2), (10),
1003, 3622; 5 U.S.C. 552b(e), (g).
5. Section 6.6 is amended by revising
the introductory text to read as follows:
■
7. The authority citation for part 7
continues to read as follows:
■
Authority: 39 U.S.C. 410; 5 U.S.C. 552b(a)–
(m).
8. Section 7.1 is amended by revising
the final sentence of paragraph (b) to
read as follows:
■
§ 6.6
Quorum and voting.
As provided by 39 U.S.C. 205(c), and
except for routine, non-controversial,
and administrative matters considered
through the notation voting process
described in § 6.7, the Board acts by
resolution upon a majority vote of those
members who attend a meeting in
person or by teleconference. No proxies
are allowed in any vote of the members
of the Board. Any 6 members constitute
a quorum for the transaction of business
by the Board, except:
*
*
*
*
*
■ 6. Section 6.7 is added to read as
follows:
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§ 6.7
§ 7.1
Definitions.
*
*
*
*
*
(b) * * * The term ’’meeting’’ does
not include any procedural
deliberations required or permitted by
§§ 6.1, 6.2, 7.4, or 7.5 of the bylaws in
this chapter, or the notation voting
process described in § 6.7 of the bylaws
in this chapter.
Stanley F. Mires,
Attorney, Legal Policy & Legislative Advice.
[FR Doc. 2012–7098 Filed 3–23–12; 8:45 am]
BILLING CODE 7710–12–P
Notation voting.
(a) General. Notation voting consists
of the circulation of written memoranda
and voting sheets to each member of the
Board simultaneously and the
tabulation of submitted responses.
Notation voting may be used only for
routine, non-controversial, and
administrative matters.
(b) Administrative Responsibility. The
Secretary of the Board is responsible for:
(1) Distributing notation voting
memoranda and voting sheets;
(2) Establishing deadlines for notation
voting sheets to be completed and
returned;
(3) Processing and tabulating all
notation voting sheets; and
(4) Determining whether further
action is required.
(c) Veto of notation voting. In view of
the public policy for openness reflected
in the Government in the Sunshine Act
and in these bylaws, each Board
member is authorized to veto the use of
notation voting for the consideration of
any matter. If a Board member vetoes
the use of notation voting, the Secretary
must notify all members of such action,
and must promptly take action to place
the particular matter on the agenda of
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ENVIRONMENTAL PROTECTION
AGENCY
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
EPA is finalizing its approval
of most of the Nevada Regional Haze
State Implementation Plan (SIP) that
implements the Clean Air Act (CAA)
Regional Haze Rule requiring states to
prevent any future and remedy any
existing man-made impairment of
visibility in mandatory Class I areas
through a regional haze program. EPA
proposed to approve all parts of
Nevada’s SIP revisions on June 22, 2011
(76 FR 36450). This final approval
applies to all aspects of Nevada’s SIP
except for that portion of Nevada’s
determination regarding the Best
SUMMARY:
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I. Background
A. Description of Regional Haze
Regional haze is the impairment of
visibility across a broad geographic area
produced by numerous sources and
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activities that emit fine particles and
their precursors, primarily sulfur
dioxide (SO2) and nitrogen oxide (NOX),
and in some cases, ammonia (NH3) and
volatile organic compounds (VOC). Fine
particle precursors react in the
atmosphere to form fine particulate
matter (PM2.5), primarily sulfates,
nitrates, organic carbon, elemental
carbon, and soil dust, which impair
visibility by scattering and absorbing
light. Visibility impairment reduces the
clarity, color, and visible distance that
one can see. PM2.5 can also cause
serious health effects and mortality in
humans and contributes to
environmental effects such as acid
deposition and eutrophication of water
bodies.
Data from existing visibility monitors,
the ‘‘Interagency Monitoring of
Protected Visual Environments’’
(IMPROVE) network, indicate that
visibility impairment caused by air
pollution occurs virtually all the time at
most federally protected national parks
and wilderness areas, known as Class I
areas. The average visual range in many
Class I areas in the western United
States is 100 to 150 kilometers, or about
one-half to two-thirds of the visual
range that would exist without manmade air pollution.1 In most of the
eastern Class I areas of the United
States, the average visual range is less
than 30 kilometers, or about one-fifth of
the visual range that would exist under
estimated natural conditions. 64 FR
35715 (July 1, 1999).
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B. History of Regional Haze Regulations
In section 169(A)(1) of the 1977
Amendments to the CAA, Congress
established as a national goal the
‘‘prevention of any future, and the
remedying of any existing, impairment
of visibility in mandatory class I Federal
areas which impairment results from
man-made air pollution.’’ Visibility was
determined by Congress to be an
important value in 156 mandatory Class
I Federal areas 2 as listed in 40 CFR
1 Visual range is the greatest distance, in
kilometers or miles, at which one can view a dark
object against the sky.
2 Areas designated as mandatory Class I Federal
areas consist of national parks exceeding 6000
acres, wilderness areas and national memorial parks
exceeding 5000 acres, and all international parks
that were in existence on August 7, 1977. 42 U.S.C.
7472(a). In accordance with section 169A of the
CAA, EPA, in consultation with the Department of
Interior, promulgated a list of 156 areas where
visibility is identified as an important value. 44 FR
69122 (November 30, 1979). Although states and
tribes may designate as Class I additional areas
which they consider to have visibility as an
important value, the requirements of the visibility
program set forth in section 169A of the CAA apply
only to ‘‘mandatory Class I Federal areas.’’ Each
mandatory Class I Federal area is the responsibility
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81.400–437. In the first phase of
visibility protection, EPA promulgated
regulations on December 2, 1980, to
address visibility impairment in Class I
areas that is ‘‘reasonably attributable’’ to
a single source or small group of
sources, i.e., ‘‘reasonably attributable
visibility impairment’’ or RAVI. 45 FR
80084. EPA deferred action on regional
haze that emanates from a variety of
sources until monitoring, modeling and
scientific knowledge about the
relationship between pollutants and
visibility impairment were improved.
Congress added section 169B to the
CAA in 1990 to conduct scientific
research on regional haze. This
legislation established the Grand
Canyon Visibility Transport
Commission (GCVTC), which issued its
report, ‘‘Recommendations for
Improving Western Vistas,’’ on June 10,
1996. These recommendations informed
the regulatory development of a regional
haze program, and provided an option
for certain western states to address
visibility at 16 Class I areas on the
Colorado Plateau under 40 CFR 51.309.
EPA promulgated a rule to address
regional haze on July 1, 1999 known as
the Regional Haze Rule (RHR). See 64
FR 35713 as amended at 70 FR 39156
(July 6, 2005) and 71 FR 60631 (October
13, 2006). The RHR revised the existing
visibility regulations to include
provisions addressing regional haze
impairment and established a
comprehensive visibility protection
program for Class I areas. The
requirements for regional haze, found at
40 CFR 51.308 and 51.309, are included
in EPA’s visibility protection
regulations at 40 CFR 51.300–309.
The requirement to submit a regional
haze SIP revision applies to all 50 states,
the District of Columbia, and the Virgin
Islands. States were required to submit
the first SIP addressing regional haze
visibility impairment no later than
December 17, 2007. 40 CFR 51.308(b).
Since most states, including Nevada,
did not submit SIPs prior to the
deadline, EPA made a Finding of
Failure to Submit that under the Clean
Air Act had the effect of creating a
deadline of January 15, 2011, for EPA to
approve a SIP or publish a Federal
Implementation Plan (FIP). 74 FR 2392
(January 15, 2009). EPA is publishing
this final action to meet this obligation
in part.
For a more detailed discussion of the
CAA and RHR requirements, please see
sections II and III of our proposal dated
June 22, 2011 (76 FR 36450). Our
of a ‘‘Federal Land Manager.’’ 42 U.S.C. 7602(i).
When we use the term ‘‘Class I area’’ in this action,
we mean a ‘‘mandatory Class I Federal area.’’
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17335
evaluation of the Nevada Regional Haze
Plan is in section IV of the same
proposal.
C. Our Proposed Action
On June 22, 2011, EPA proposed to
approve all portions of Nevada’s
Regional Haze SIP as meeting the
relevant requirements of CAA Section
169A and the Regional Haze Rule. We
proposed to find that Nevada
appropriately established baseline
visibility conditions and a reasonable
progress goal for its one Class I area;
developed a long-term strategy with
enforceable measures to ensure
reasonable progress toward achieving
the Reasonable Progress Goal in the first
planning period ending in 2018;
adequately applied Best Available
Retrofit Technology to specific
stationary sources, including RGGS;
developed a regional haze monitoring
strategy; provided for periodic progress
reports and revisions; provided for
consultation and coordination with
federal land managers; and provided for
the regional haze SIP’s future review
and revisions. We also proposed to find
that emissions from Nevada do not
interfere with other states’ measures to
protect visibility as required by CAA
Section 110(a)(2)(D)(i)(II). Our proposed
action provides more information about
the relevant CAA requirements, EPA
guidance, the State’s submittals, and our
review and evaluation of the SIP
revisions.
II. BART Determination for NOX at
Reid Gardner
We are taking no action in today’s
rule on the portion of the Nevada SIP
that contains the BART determination at
RGGS for NOX. Following our review of
the public comments on this issue, we
performed additional analysis of
Nevada’s NOX BART determination for
RGGS. As a result, we no longer
consider the currently available
information to be sufficient for us to
take final action on the Nevada Division
of Environmental Protection’s (NDEP’s)
determination that rotating overfire air
(ROFA) with Rotamix (a form of
selective non-catalytic reduction or
SNCR) is the NOX control technology
that represents BART. We intend to
consider this determination in more
detail at a future date.
A. Background
The RHR provides that a BART
determination must take into account
several factors, which are frequently
referred to as the ‘‘five-factor analysis.’’
These factors are listed below (40 CFR
51.308(e)(1)(ii)(A)):
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• The cost of compliance for the
technically feasible control
technologies;
• The energy and non-air quality
impacts of the control technologies;
• Any existing air pollution control
technologies at the source;
• The remaining useful life of the
source; and
• The degree of visibility
improvement which may reasonably be
anticipated to result from the various
control technologies.
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B. NDEP’s Determination
RGGS consists of four coal-fired
boilers, three of which are BARTeligible units with generating capacity
of 100 megawatts (MW) each. A fourth
unit (250 MW) is not BART-eligible.
Nevada Energy, the owner of RGGS,
performed a BART analysis for the three
BART-eligible RGGS units and
submitted the results of its analysis to
NDEP.3 In its BART analysis, Nevada
Energy considered several NOX control
technologies and evaluated the cost of
compliance and visibility improvement
associated with each technology. In
preparing the SIP, NDEP relied on
certain aspects of Nevada Energy’s
analysis while performing updated
analyses for other aspects. When
considering the cost and cost
effectiveness of compliance, NDEP
developed its own set of emission
reduction estimates for the various NOX
control technologies, but used Nevada
Energy’s estimates of total capital and
annual costs.4 When considering the
degree of visibility improvement
associated with various control
technologies, NDEP relied upon the
visibility impacts for each control
option as modeled by Nevada Energy,
rather than modeling the visibility
impacts attributable to NDEP’s own
estimates of NOX removal.
In its submittal to NDEP, Nevada
Energy determined that low NOX
burners (LNB) with OFA (overfire air)
were BART for NOX. In preparing the
SIP, NDEP determined that a more
stringent control technology, ROFA
with Rotamix, was BART for NOX.
NDEP eliminated even more stringent
control options, such as Selective
3 Nevada Energy BART Analysis Reports,
Reid_Gardner_1_10–03–08.pdf,
Reid_Gardner_2_10–03–08.pdf,
Reid_Gardner_3_10–03–08.pdf. Available in Docket
Item No. EPA–R09–OAR–2011–0130–0007.
4 Based on a comparison of emission reductions
summarized in Table 1, NDEP Reid Gardner BART
Determination, October 22, 2009 (Available as
Docket Item No. EPA–R09–OAR–2011–0130–0005),
and emission reductions summarized in Table 3–2
of the NVE BART Analysis Reports. Visibility
impacts as summarized from Table 5–4 of the NVE
BART Analysis Reports.
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Catalytic Reduction (SCR) with LNB and
OFA, on the grounds that ‘‘the $/ton of
NOX removed increased significantly
* * * without correspondingly
significant improvements in
visibility.’’ 5
C. Public Comments Relevant to NDEP’s
Determination
As noted in Section II.B above,
NDEP’s elimination of control options
more stringent than ROFA with Rotamix
was based on the incremental cost
effectiveness ($/ton) and expected
visibility improvement of the various
options. EPA received several comments
(see Docket Items 0054, 0057, 0061,
0062 and 0062 Attachment 6) alleging
flaws in NDEP’s analysis and response
to comments, and stating that SCR
should be BART for NOX at RGGS.
These commenters alleged certain flaws
and submitted additional information in
criticizing NDEP’s development of the
cost effectiveness values and expected
visibility improvement attributable to
the more stringent SCR-based control
option.
Regarding cost effectiveness, several
commenters (see Docket Items 0054,
0057, 0061, and 0062) alleged that the
total capital and annual cost estimates
relied upon by NDEP for the SCR-based
control options were overestimated,
included several costs not allowed by
EPA’s Control Cost Manual (CCM) such
as owner’s costs, surcharge, and
allowance for funds used during
construction (AFUDC), and used certain
variables and values that were either
inflated or unreasonable. One
commenter (see docket item 0062
Attachment 6) performed a revised
analysis of SCR cost effectiveness that
adjusted for these alleged issues, and
projected a 33 to 40 percent decrease in
average and incremental cost
effectiveness values as a result of these
adjustments. In addition, commenters
stated that total capital and annual cost
estimates lacked evidentiary support in
the administrative record due to the
absence of detailed information such as
equipment design parameters,
equipment lists, and actual cost
calculations. Finally, commenters also
stated that the level of SCR performance
relied upon by NDEP is not supported
in the administrative record by sitespecific information such as vendor
quotes or specifications (see Docket
Items 0054 and 0061 to 0063).
5 Revised NDEP Reid Gardner BART
Determination Review, page 6. Available as Docket
Item No. EPA–R09–OAR–2011–0130–0005. See also
Nevada Regional Haze SIP, Appendix D (Responses
to Comments), pages D–32 to –42. Available in
docket item No. EPA–R09–OAR–2011–0130–003.
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Regarding visibility improvement,
commenters (see Docket Items 0054 and
0062) noted that while baseline
visibility modeling indicated that RGGS
currently causes or contributes to
visibility impairment at multiple Class I
areas, control scenario visibility
modeling results were only provided for
the single closest Class I area, Grand
Canyon National Park. They asserted
that the potential visibility benefit at all
affected Class I areas should be
accounted for when considering control
technology options. In addition, as
described in Section II.B above, NDEP
estimated larger NOX emission
reductions than the emission reductions
estimated by Nevada Energy. NDEP,
however, continued to rely on the
visibility modeling provided by Nevada
Energy, and did not update the
modeling to reflect NDEP’s larger NOX
emission reduction estimates. As a
result, the existing visibility modeling
does not reflect the incremental
visibility improvement attributable to
NDEP’s estimates of NOX emission
reductions. Finally, commenters noted
that certain modeling files and
documentation were missing from our
docket and were unavailable from
NDEP, such as the NOX control scenario
modeling result files and supporting
information for NDEP’s baseline
emission scenarios.
D. EPA’s Analysis
After reviewing the public comments,
we performed additional analysis of the
cost effectiveness and visibility
improvement associated with the
various NOX control technologies
considered by NDEP in determining
BART at RGGS. Based upon this
additional analysis, we no longer
consider the currently available
supporting information to be
sufficiently detailed to allow us to
perform a critical review of these issues.
As a result, we are taking no action in
this rule on NDEP’s determination that
ROFA with Rotamix is the NOX control
technology that represents BART.
Therefore, EPA is taking no action on
the portion of the SIP containing the
BART determination for NOX at RGGS
including the corresponding emission
limits and schedules of compliance for
NOX at RGGS in the SIP’s long-term
strategy. Specifically, these are sections
5.5.3, 5.6.3 and 7.2 of Nevada’s SIP that
address the NOX BART control analyses,
visibility improvement, and
implementation at RGGS. Since the
emissions inventories used to develop
the reasonable progress goal (RPG) did
not include NOX reductions from BART,
the fact that we take no action in this
rule regarding the RGGS BART
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determination for NOX does not impact
the RPG, and will not require
adjustments to the long-term strategy
(LTS) in the SIP.6 EPA will propose
further action on this particular portion
of the SIP in the future.
III. EPA Responses to Public Comments
Except BART for NOX at RGGS
EPA’s proposed approval published
on June 22, 2011 (76 FR 36450)
included a 30-day public comment
period, which ended on July 22, 2011.
We subsequently extended the comment
period by 30 days until August 22, 2011
(76 FR 43963). We received comments
from WildEarth Guardians, a
consortium of environmental and
conservation organizations 7
(‘‘Consortium’’), the Moapa Band of
Paiutes, the Nevada Division of
Environmental Protection (NDEP), the
National Park Service, the U.S. Fish and
Wildlife Service, and seven individuals.
With the exception of NDEP’s
comments, which support EPA’s
proposed approval of its plan, most of
the comments expressed opposition to
EPA’s full approval of the SIP. The
majority of these comments criticized
our proposed approval of NDEP’s
determination of BART controls to
reduce emissions of NOX at RGGS. In
this final rule approving all other
portions of Nevada’s RH SIP, we are
responding to all other major comments
on our proposed SIP approval. We find
that the SIP is approvable except BART
for NOX at RGGS on which EPA is
taking no action.
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A. Reasonable Progress Goal
Comments: The National Park Service
and U.S. Fish and Wildlife Service
expressed concern that the SIP’s
reasonable progress analysis was not
consistent with Section 308(d)(1) of the
Regional Haze Rule and EPA’s Guidance
for Setting Reasonable Progress Goals
under the Regional Haze Program
because NDEP ‘‘did not consider what
additional emissions reductions beyond
those already being implemented might
be reasonable to improve visibility.’’
Similarly, WildEarth Guardians
commented that the Clean Air Act
requires EPA to base reasonable
progress goals on the factors set forth
under Section 169A(g), and not the bare
minimum required to meet the uniform
6 Per the Nevada RH SIP, page 6–5, the only
BART emission reductions included in the 2018
emission inventory were SO2 reductions resulting
from presumptive BART limits.
7 The Consortium’s comment letter was signed by
representatives of the Sierra Club, National Parks
Conservation Association, Citizens for Dixie’s
Future, Defend Our Desert, Friends of Gold Butte,
Grand Canyon Trust, and Western Resource
Advocates.
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rate of progress. WildEarth Guardians
expressed concern that ‘‘EPA has
overlooked opportunities to further
reduce haze forming pollution from
sources in Nevada.’’ By contrast, NDEP
asserted that its reasonable progress
analysis considered the four factors
required under the Regional Haze Rule
(i.e., the costs of compliance, the time
necessary for compliance, the energy
and non-air quality environmental
impacts of compliance, and the
remaining useful life of any existing
source subject to such requirements).
Specifically, NDEP noted that ‘‘[c]ost
was considered first, * * * and the
NDEP concluded it was not necessary to
continue with an analysis of the
remaining factors.’’
Response: As explained in the
proposed rule, in promulgating the SIP
NDEP considered the four factors in
setting the reasonable progress goal for
the Jarbidge Wilderness Area, the only
Class I area in Nevada. The RHR and
EPA’s guidance affords the State
considerable flexibility in determining
whether additional emission reduction
measures are needed to achieve the RPG
in the first planning period. The NDEP
reasonably concluded that the cost of
additional controls was not warranted
given projected emissions reductions
from anthropogenic sources and the fact
that the majority of haze at Jarbidge is
from natural and out-of-state sources.
Moreover, NDEP noted in its comments
that ‘‘of the five proposed electrical
generating units (EGUs) included in the
State’s 2018 emissions inventory, only
two have moved forward and are now
operational,’’ which would further
lower emissions projections for both
NOX and SO2 by 2018. The comments
do not demonstrate that the State failed
to consider reasonably the four factors,
but the comments question whether the
State should have done a more robust
analysis. EPA has considered the
comments and the comments have not
provided any further specific facts that
should have been considered in the
State’s analysis beyond conclusory
criticisms. Therefore, given the broad
discretion the RHR affords the State,
and the lack of specificity in the
comments on this issue, EPA reaffirms
its proposed decision to approve the
State’s reasonable progress goal for
Jarbidge.
B. Long-Term Strategy
Comments: The Consortium argued
that the SIP ‘‘does not contain evidence
showing full and effective consultation
with other states, does not ‘ensure that
it has included all measures needed to
achieve its apportionment of emission
reduction obligations agreed upon’
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17337
through that consultation process and
further fails to ‘document the technical
basis, including modeling, monitoring
and emissions information,’ on which it
relies to determine its apportionment of
emission reduction obligations agreed
upon through that process.’’
Specifically, the Consortium noted that,
‘‘[a]lthough the Proposed SIP implies
that Nevada consulted with the Western
Regional Air Partnership (‘‘WRAP’’) in
determining its apportionment of
visibility impacts to Class I areas
outside of the State of Nevada, the
administrative record does not support
the legally-required level of
consultation.’’ They further argued that
‘‘WRAP’s failure to apportion Nevada’s
contribution does not save Nevada from
its independent obligation to require
adequate BART determinations and a
long-term strategy to reduce hazecausing pollutants in out-of-state Class I
areas from its pollution sources.’’
Response: EPA disagrees with the
assertions that Nevada did not consult
with other states, did not meet its source
apportionment obligations to Class I
areas in other states, and did not
document the technical basis for its
apportionment as required in 40 CFR
51.308(d)(3)(i), (ii), and (iii). Although
Nevada lacked formal membership in
the WRAP, representatives from NDEP
actively participated with other state
representatives in the WRAP’s
committees and work groups, which
jointly directed the development of the
WRAP’s technical analyses. Nevada and
other western states relied on the
WRAP’s source apportionment
modeling results to estimate the
contribution of out-of-state emissions
and relied on the WRAP’s consultation
process to ensure the compatibility of
reasonable progress goals and long-term
strategies.8 Nevada used the WRAP’s
source apportionment modeling to
demonstrate the minimal contribution
of Nevada’s emissions to sulfate and
nitrate extinction at 25 Class I areas in
five neighboring states.9 Based on
consultation through the WRAP, Nevada
identified no major contributions that
supported developing new interstate
strategies, mitigation measures, or
emissions reduction obligations. Nevada
and neighboring states agreed that the
implementation of BART and other
existing measures in state regional haze
plans were sufficient for the states to
meet the reasonable progress goals for
their respective Class I areas, and that
future consultation would address any
8 See 9.1.3 Past Consultation with other States in
Nevada’s SIP.
9 See 4.3.3 Source Apportionment for Other Class
I Areas in Nevada’s SIP.
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new strategies or measures needed.
Moreover, Nevada did not receive any
requests from other states to achieve
even greater reductions in its emissions
in order for other states to meet their
RPGs. Therefore, EPA reaffirms its
proposed determination that Nevada
adequately consulted with other states,
demonstrated that its SIP includes all
measures necessary to obtain its share of
emission reductions at other Class I
areas, and provided the technical basis
to document its analysis.
C. BART for SO2 and PM10 at RGGS
In addition to extensive comments
addressing NDEP’s BART determination
for NOX at RGGS, we also received
comments concerning the timing of
implementation of BART at RGGS
generally, as well as comments
specifically addressing the SO2 and
PM10 BART determinations for RGGS.
As noted above, we are not acting on
NDEP’s BART determination for NOX at
RGGS at this time. Therefore, our
responses concerning RGGS are limited
to comments related to the SO2 and
PM10 BART determinations.
sroberts on DSK5SPTVN1PROD with RULES
1. BART for SO2 at RGGS
Comments: Regarding NDEP’s BART
determination for SO2 at RGGS,
WildEarth Guardians expressed concern
that ‘‘SO2 limits do not appear to
represent the degree of reduction
achievable through the application of
the best system of continuous emission
reduction.’’ In particular, they asserted
that ‘‘it appears that Reid Gardner is
already meeting emission limits that are
less than half of this proposed limit’’,
and that ‘‘even Nevada recognizes the
SO2 emissions increases will occur as a
result of [NDEP’s] proposed BART.’’ By
contrast, the National Park Service and
the U.S. Fish and Wildlife Service
praised ‘‘NDEP’s action to lower the SO2
limit’’ at RGGS.
Response: In setting the SO2 BART
limits for RGGS, NDEP took into
account the existing controls at the
facility, consistent with CAA Section
169A(g)(2) and 40 CFR
51.308(e)(1)(ii)(A). In particular, NDEP
considered the effect of new fabric filter
baghouses that were installed on all
three BART units at RGGS in 2008 and
2009 pursuant to a consent decree
between the facility’s owner and NDEP
and EPA.10 The consent decree
established an SO2 emissions limit of
0.40 lbs/MMbtu (a million British
thermal units), based on a 10-day rolling
average period, for each of the three
10 See
Nevada’s RH SIP Sections 5.5 and 6.5.2.2.
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BART units.11 In its draft regional haze
SIP, NDEP proposed an SO2 emissions
limit of 0.25 lbs/MMbtu for each of the
three BART units at RGGS. In response
to comments from EPA and the National
Park Service, NDEP subsequently
lowered the BART limits to 0.15 lbs/
MMbtu, based on a 24-hour averaging
period.12
In arguing for further reductions in
these BART limits, WildEarth Guardians
notes that, ‘‘according to Clean Air
Markets data from the EPA, units 1–3
are meeting annual sulfur dioxide
emission rates of between 0.054 and
0.064 lbs/MMbtu and have for at least
the last two years.’’ However, while the
units’ current annual average emission
rates may be less than 0.15 lb/MMbtu,
these figures are not directly comparable
to the 24-hour rolling average emissions
limits set by NDEP in its BART
determination for RGGS. The more
relevant points of comparison are the
units’ current Title V permit limits of
0.40 lbs/MMbtu, based on a 10-day
rolling average period, which are more
than twice the limit that NDEP has set
for each of the three BART units in its
Regional Haze SIP.
In response to commenters’ concerns
regarding potential increases in SO2
emissions as a result of NDEP’s BART
determination at RGGS, EPA reexamined NDEP’s estimates of emission
reductions resulting from BART
controls at RGGS. Nevada’s SIP provides
two sets of estimated emission
reductions resulting from BART
controls at RGGS, one based on the
WRAP baseline (4,970 tons) and one
based on NDEP’s baseline (1,441 tons)
for SO2.13 Although SO2 emissions are
estimated to increase by 838 tons from
NDEP’s baseline, they are expected to
decrease by 2,696 tons from the WRAP’s
baseline. Under both scenarios, the
emissions after BART Controls are held
constant at 2,279 tons. Thus, the
difference in estimated emissions
reductions is a reflection of the large
difference between the WRAP baseline
and the NDEP baseline for SO2.
NDEP’s baseline emissions for SO2
were calculated using acid rain data that
omitted data deemed invalid due to
monitoring problems that were
addressed by the consent decree.
According to NDEP, the omission of the
invalid data effectively lowered the
baseline emissions (measured in lbs/
MMbtu) by nearly half.14 Thus, the
11 United States v. Nevada Power Company, Case
2:07–cv–00417 (D. Nev.) (consent decree entered
June 15, 2007).
12 See Nevada’s RH SIP Chapter 5, footnote 4.
13 See Nevada’s RH SIP, Table 5–6 Reid Gardner:
BART Emissions Reductions in Tons per Year.
14 See Nevada’s RH SIP Section 5.5.
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projected increase in SO2 appears to be
an artifact of NDEP’s exceptionally low
baseline that is attributable to the
exclusion of invalid data.
From a broader perspective, NDEP’s
BART determination for SO2 at RGGS
will result in a lower emissions limit
(0.15 lbs/MMbtu based on a 24-hour
rolling average compared to the current
Title V Permit limit of 0.40 lbs/MMbtu
based on a 10-day rolling average
period) related to the new fabric filter
baghouses and existing wet soda ash
with a dry flue gas desulfurization
system. Since the BART determination
lowers the short-term emissions limit,
there is no valid reason to suspect that
SO2 emissions will increase as a result
of BART controls. EPA will use the
progress report due five years after the
SIP’s approval to evaluate actual SO2
emissions at RGGS to ensure that
NDEP’s BART determination has not
resulted in increased emissions and will
encourage NDEP to take appropriate
action, if necessary, at that time.
2. BART for PM10 at RGGS
Comments: Regarding the PM10 limit,
WildEarth Guardians expressed concern
that ‘‘the proposed BART determination
is unenforceable because there are no
monitoring, recordkeeping, or reporting
requirements proposed that would
ensure compliance with the 24-hour
limits. There are simply no monitoring
requirements proposed that would
actually ensure that the PM limit is met
on a continuous basis. This is contrary
to the Clean Air Act, which defines
BART based on continuous emission
reductions.’’
Response: As explained in EPA’s
BART Guidelines, ‘‘[m]onitoring
requirements generally applicable to
sources, including those that are subject
to BART, are governed by other
regulations. See, e.g., 40 CFR part 64
(compliance assurance monitoring); 40
CFR 70.6(a)(3) (periodic monitoring); 40
CFR 70.6(c)(1) (sufficiency
monitoring).’’ 15 The monitoring,
recordkeeping and reporting
requirements specifically applicable to
RGGS are found in the existing Nevada
SIP as well as the facility’s Title V
permit. In particular, the applicable SIP
requires continuous monitoring of
opacity and compliance with a 20
percent opacity limit.16 Although
opacity does not directly correlate with
particulate concentrations, it is a good
indicator of proper operation of the
baghouse since almost any opacity from
a baghouse-controlled coal-fired boiler
15 40
CFR part 51 Appendix Y, Section V.
40 CFR 52.1470(c); Nevada Administrative
Code 445B.256–267, 22017.
16 See
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is indicative of leaks in the baghouse.
Under Part 64, such an excursion or
exceedance must be addressed ‘‘as
expeditiously as practicable in
accordance with good air pollution
control practices for minimizing
emissions.’’ 17 For directly assuring
compliance with existing PM10 limits,
the Title V permit for RGGS contains an
annual stack test requirement using
Method 5 for PM and Method 201A/202
for PM10. Given the current opacity limit
in the SIP and the compliance methods
in RGGS’s Title V permit, we are
approving the BART determination for
PM10 in Nevada’s RH SIP. We will
continue to work with Nevada to ensure
that all appropriate compliance
provisions are in the SIP.
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3. Timing of Implementation
Comments: WildEarth Guardians
expressed concern that ‘‘EPA has not
demonstrated that ‘by January 1, 2015’
is as expeditiously as practical for
complying with BART at Reid Gardner,
nor shown that it is reasonable to allow
the facility a full five years to come into
compliance with BART.’’
Response: The Nevada BART
regulation in the Regional Haze SIP
requires that the BART control measures
at RGGS must be installed and operating
‘‘[o]n or before January 1, 2015; or (2)
[n]ot later than 5 years after approval of
Nevada’s state implementation plan for
regional haze by the United States
Environmental Protection Agency
Region 9, whichever occurs first.’’ Given
the date of our approval of Nevada’s
SIP, the BART implementation deadline
for the RGGS is January 1, 2015, about
three years from the date of this final
rule. EPA considers Nevada’s choice of
the January 1, 2015, to be reasonable in
this instance.
D. Corrections to EPA’s Technical
Analysis
Comments: NDEP noted a few
corrections to EPA’s analysis in the
proposed rule at 76 FR 36450 (June 22,
2011), but stated that these minor
corrections do not alter any of EPA’s
conclusions. The first correction was to
note that the percentages of emissions
by source category shown in section
IV.C.2 of EPA’s proposed rule are based
on the 2018 emissions inventory. The
proposal omitted the date of the
inventory. Secondly, NDEP commented
that the discussion of predominant
sources of PM2.5 was in error because
‘‘the predominant source of PM fine
emissions are windblown dust (43
percent) and fugitive dust (30 percent).’’
EPA had mistakenly attributed PM fine
17 40
CFR 64.7(d)(1).
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emissions to natural fires (49 percent)
and area sources (37 percent). Lastly,
NDEP commented on the sources of
visibility impairment, saying that soil in
PM2.5 is mostly from windblown dust,
not natural fire. EPA had mistakenly
attributed the source of PM2.5 to natural
fire.
Response: EPA is correcting the
record as noted above.
IV. EPA Action
Under section 110(k)(3) of the CAA,
EPA is fully approving most portions of
the Nevada Regional Haze SIP as
satisfying all of the relevant
requirements of CAA Section 169A and
the Regional Haze Rule. For the portions
of the SIP establishing BART for NOX at
RGGS, EPA is taking no action at this
time, and will take action on those
portions of the SIP in a separate
rulemaking.
We find that Nevada has met the
following Regional Haze Rule
requirements: The State established
baseline visibility conditions and
reasonable progress goals for each of its
Class I areas; the State developed a longterm strategy with enforceable measures
ensuring reasonable progress towards
meeting the reasonable progress goals
for the first ten-year planning period,
through 2018; the State has adequately
addressed the application of Best
Available Retrofit Technology to
specific stationary sources, except for
NOX at RGGS; the State has an adequate
regional haze monitoring strategy; the
State provided for consultation and
coordination with federal land managers
in producing its regional haze plan; and,
the State provided for the regional haze
plan’s future revisions.
In addition, under section 110(k)(3) of
the CAA, we are fully approving the
Nevada Regional Haze SIP as satisfying
the CAA Section 110(a)(2)(D)(i)(II)
requirement to prohibit emissions that
will interfere with measures to protect
visibility in another state for the 1997 8hour ozone and 1997 PM2.5 NAAQS.18
V. Statutory and Executive Order
Reviews
Under the Clean Air Act, the
Administrator is required to approve a
SIP submission that complies with the
provisions of the Act and applicable
Federal regulations. 42 U.S.C. 7410(k);
40 CFR 52.02(a). Thus, in reviewing SIP
18 As noted in our proposal, 76 FR 36465, we
previously approved Nevada’s SIP for Interstate
Transport as meeting the other requirements of
CAA section 110(a)(2)(D)(i) for the 1997 8-hour
ozone and 1997 PM2.5 NAAQS. See 70 FR 41629.
We are now codifying this prior approval along
with our current approval under a new section
entitled ‘‘Interstate Transport.’’
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17339
submissions, EPA’s role is to approve
State choices, provided that they meet
the criteria of the Clean Air Act.
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 Clean Air Act;
and
• Does not interfere with Executive
Order 12898 (59 FR 7629 (Feb. 16,
1994)) because EPA lacks the
discretionary authority to address
environmental justice in this
rulemaking.
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. However, the Moapa Band of
Paiutes did raise issues in the context of
the BART determination for RGGS,
which will be addressed at a future date.
Region 9 engaged in formal consultation
with the Moapa Band of Paiutes on
August 11, 2011, and heard these issues
in person. We will continue to consult
with Moapa on RGGS.
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Federal Register / Vol. 77, No. 58 / Monday, March 26, 2012 / Rules and Regulations
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 Clean
Air Act, petitions for judicial review of
this action must be filed in the United
States Court of Appeals for the
appropriate circuit by May 25, 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 may
not be challenged later in proceedings to
enforce its requirements (see section
307(b)(2)).
PART 52—[AMENDED]
1. The authority citation for part 52
continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
Subpart DD—Nevada
2. In § 52.1470(c):
a. In paragraph (c), Table 1 is
amended by adding an entry for
‘‘445B.029’’ after the entry for
‘‘445B.022’’, and adding entries for
‘‘445B.22095,’’ and ‘‘445B.22096’’ after
the entry for ‘‘445B.22093’’.
■
■
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Incorporation by
reference, Intergovernmental relations,
Nitrogen oxides, Sulfur dioxide,
Particulate matter, Reporting and
recordkeeping requirements, Visibility,
Volatile organic compounds.
Dated: December 13, 2011.
Jared Blumenfeld,
Regional Administrator, Region 9.
Part 52, chapter I, title 40 of the Code
of Federal Regulations is amended as
follows:
3. The table in paragraph (e) is
amended by adding an entry for
‘‘Nevada Regional Haze State
Implementation Plan (October 2009)’’ to
the end of the table.
■
§ 52.1470
*
Identification of plan.
*
*
(c) * * *
*
*
TABLE 1—EPA-APPROVED NEVADA REGULATIONS
State citation
Title/subject
State effective
date
Additional
explanation
EPA approval date
Nevada Administrative Code, Chapter 445B, Air Controls, Air Pollution; Nevada Administrative Code, Chapter 445, Air Controls, Air
Pollution; Nevada Air Quality Regulations—Definitions
*
*
*
445B.029 ................................. ‘‘Best available retrofit technology’’ defined.
*
4/23/09
*
[Insert page number where
the document begins 3/26/
12].
*
*
Included in supplemental SIP
revision submitted on September 20, 2011, and approved as part of approval
of Nevada Regional Haze
SIP.
*
*
*
445B.22095 ............................. Emission limitation for BART
*
4/23/09
*
[Insert page number where
the document begins 3/26/
12].
*
445B.22096, excluding the
NOX emission limits and
control types in sub-paragraph (1)(c).
1/28/10
[Insert page number where
the document begins 3/26/
12].
*
Included in supplemental SIP
revision submitted on September 20, 2011, and approved as part of approval
of Nevada Regional Haze
SIP.
Included in supplemental SIP
revision submitted on September 20, 2011, and approved as part of approval
of Nevada Regional Haze
SIP. Excluding the NOX
emission limits and control
types for units 1, 2 and 3 of
NV Energy’s Reid Gardner
Generating Station.
sroberts on DSK5SPTVN1PROD with RULES
*
*
*
Control measures constituting
BART; limitations on emissions.
*
*
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*
*
*
16:21 Mar 23, 2012
*
*
*
(e) * * *
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Federal Register / Vol. 77, No. 58 / Monday, March 26, 2012 / Rules and Regulations
Applicable geographic or
nonattainment area
Name of SIP provision
State submittal
date
*
*
*
State-wide ..............................
Nevada Regional Haze State
Implementation Plan (October 2009), excluding the
BART determination and the
associated emission limits
for NOX at Reid Gardner
Generating Station in sections 5.5.3, 5.6.3 and 7.2.
*
*
*
3. Section 52.1488 is amended by
adding paragraph (e) to read as follows:
■
§ 52.1488
*
11/18/09
EPA approval date
*
[Insert page number where
the document begins 3/26/
12].
*
*
on February 18, 2010 and September 20,
2011.
[FR Doc. 2012–7025 Filed 3–23–12; 8:45 am]
Visibility protection.
BILLING CODE 6560–50–P
*
*
*
*
*
(e) Approval. On November 18, 2009,
the Nevada Division of Environmental
Protection submitted the ‘‘Nevada
Regional Haze State Implementation
Plan.’’ With the exception of the BART
determination and the associated
emission limits for NOX at Reid Gardner
Generating Station in sections 5.5.3,
5.6.3 and 7.2, the Nevada Regional Haze
State Implementation Plan, as
supplemented and amended on
February 18, 2010 and September 20,
2011, meets the applicable requirements
of Clean Air Act sections 169A and
169B and the Regional Haze Rule in 40
CFR 51.308.
4. Add a new § 52.1491 to read as
follows:
■
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§ 52.1491
(a) Approval. On February 7, 2007,
the Nevada Division of Environmental
Protection submitted the ‘‘Nevada State
Implementation Plan for Interstate
Transport to Satisfy the Requirements of
the Clean Air Act 110(a)(2)(D)(i) for the
8-hour Ozone and PM2.5 NAAQS
Promulgated in July 1997’’ (‘‘2007
Interstate Transport SIP’’). The 2007
Interstate Transport SIP meets the
requirements of Clean Air Act section
110(a)(2)(D)(i) for the 1997 8-hour ozone
and 1997 PM2.5 NAAQS other than the
requirements of Clean Air Act section
110(a)(2)(D)(i)(II) regarding interference
with other states’ measures to protect
visibility.
(b) Approval. The requirements of
Clean Air Act section 110(a)(2)(D)(i)(II)
regarding interference with other states’
measures to protect visibility for the
1997 8-hour ozone and 1997 PM2.5
NAAQS are met by the ‘‘Nevada
Regional Haze State Implementation
Plan,’’ as supplemented and amended
16:21 Mar 23, 2012
40 CFR Part 52
[EPA–R03–OAR–2011–0713; FRL–9652–6]
Approval and Promulgation of Air
Quality Implementation Plans;
Delaware, Maryland, New Jersey, and
Pennsylvania; Determinations of
Attainment of the 1997 8-Hour Ozone
Standard for the PhiladelphiaWilmington-Atlantic City Moderate
Nonattainment Area
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
EPA is making two
determinations regarding the
Philadelphia-Wilmington-Atlantic City,
PA–NJ–MD–DE 8-hour ozone moderate
nonattainment area (the Philadelphia
Area). First, EPA is determining that the
Philadelphia Area has attained the 1997
8-hour ozone National Ambient Air
Quality Standard (NAAQS). This
determination is based upon complete,
quality assured, and certified ambient
air monitoring data that show the area
has monitored attainment of the 1997 8hour ozone NAAQS for the 2008–2010
monitoring period. In accordance with
EPA’s applicable ozone implementation
rule, this clean data determination
suspends the requirement for the
Philadelphia Area to submit an
attainment demonstration, reasonably
available control measures (RACM), a
reasonable further progress (RFP) plan
and contingency measures related to
attainment of the 1997 8-hours ozone
NAAQS. These requirements shall be
suspended for so long as the area
continues to attain the 1997 8-hour
ozone NAAQS. Second, EPA is
SUMMARY:
Interstate transport.
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ENVIRONMENTAL PROTECTION
AGENCY
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Explanation
*
*
*
Excluding Appendix A (‘‘Nevada BART Regulation’’).
The Nevada BART regulation, including NAC
445B.029, 445B.22095,
and 445B.22096, is listed
above in 40 CFR
52.1470(c).
*
determining that the Philadelphia Area
has attained the 1997 8-hour ozone
NAAQS by its attainment date of June
15, 2011. These actions are being taken
under the Clean Air Act (CAA).
DATES: Effective Date: This final rule is
effective on April 25, 2012.
ADDRESSES: EPA has established a
docket for this action under Docket ID
Number EPA–R03–OAR–2011–0713. 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.
FOR FURTHER INFORMATION CONTACT: If
you have questions concerning EPA’s
proposed action related to Delaware,
Maryland or Pennsylvania, please
contact Maria A. Pino (215) 814–2181,
or by email at pino.maria@epa.gov. If
you have questions concerning EPA’s
proposed action related to New Jersey,
please contact Paul Truchan (212) 637–
3711, or by email at
truchan.paul@epa.gov.
SUPPLEMENTARY INFORMATION: The
following outline is provided to aid in
locating information in this action.
I. Background
II. Summary of Actions
III. Final Action
IV. Statutory and Executive Order Reviews
I. Background
EPA published a notice of proposed
rulemaking (NPR) for the States of
Delaware, Maryland, and New Jersey
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Agencies
[Federal Register Volume 77, Number 58 (Monday, March 26, 2012)]
[Rules and Regulations]
[Pages 17334-17341]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2012-7025]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R09-OAR-2011-0130, FRL-9612-7]
Approval and Promulgation of Air Quality Implementation Plans;
State of Nevada; Regional Haze State Implementation Plan
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: EPA is finalizing its approval of most of the Nevada Regional
Haze State Implementation Plan (SIP) that implements the Clean Air Act
(CAA) Regional Haze Rule requiring states to prevent any future and
remedy any existing man-made impairment of visibility in mandatory
Class I areas through a regional haze program. EPA proposed to approve
all parts of Nevada's SIP revisions on June 22, 2011 (76 FR 36450).
This final approval applies to all aspects of Nevada's SIP except for
that portion of Nevada's determination regarding the Best Available
Retrofit Technology (BART) to reduce nitrogen oxide (NOX)
emissions at the Reid Gardner Generating Station (RGGS). We will take
action on BART for NOX at RGGS in a future notice.
DATES: Effective Date: This rule is effective on April 25, 2012.
ADDRESSES: EPA has established docket number EPA-R09-OAR-2011-0130 for
this action. Generally, documents in the docket are available
electronically at https://www.regulations.gov or in hard copy at EPA
Region 9, 75 Hawthorne Street, San Francisco, California. Please note
that while many of the documents in the docket are listed at https://www.regulations.gov, some information may not be specifically listed in
the index to the docket and may be publicly available only at the hard
copy location (e.g., copyrighted material, large maps, multi-volume
reports or otherwise voluminous materials), and some may not be
available at either locations (e.g., confidential business
information). To inspect the hard copy materials, please schedule an
appointment during normal business hours with the contact listed
directly below.
FOR FURTHER INFORMATION CONTACT: Thomas Webb, U.S. EPA, Region 9,
Planning Office, Air Division, Air-2, 75 Hawthorne Street, San
Francisco, CA 94105. Thomas Webb can be reached at telephone number
(415) 947-4139 and via electronic mail at webb.thomas@epa.gov.
SUPPLEMENTARY INFORMATION: Throughout this document, wherever ``we,''
``us,'' or ``our,'' is used, we mean the United States Environmental
Protection Agency (EPA).
Table of Contents
I. Background
A. Description of Regional Haze
B. History of Regional Haze Regulations
C. Our Proposed Action
II. BART Determination for NOX at Reid Gardner
A. Background
B. NDEP's Determination
C. Public Comments Relevant to NDEP's Determination
D. EPA's Analysis
III. EPA Responses to Public Comments Except BART for NOX
at RGGS
A. Reasonable Progress Goal
B. Long-Term Strategy
C. BART for SO2 and PM10 at Reid Gardner
D. Corrections to EPA's Technical Analysis
IV. EPA Action
V. Statutory and Executive Order Reviews
I. Background
A. Description of Regional Haze
Regional haze is the impairment of visibility across a broad
geographic area produced by numerous sources and
[[Page 17335]]
activities that emit fine particles and their precursors, primarily
sulfur dioxide (SO2) and nitrogen oxide (NOX),
and in some cases, ammonia (NH3) and volatile organic
compounds (VOC). Fine particle precursors react in the atmosphere to
form fine particulate matter (PM2.5), primarily sulfates,
nitrates, organic carbon, elemental carbon, and soil dust, which impair
visibility by scattering and absorbing light. Visibility impairment
reduces the clarity, color, and visible distance that one can see.
PM2.5 can also cause serious health effects and mortality in
humans and contributes to environmental effects such as acid deposition
and eutrophication of water bodies.
Data from existing visibility monitors, the ``Interagency
Monitoring of Protected Visual Environments'' (IMPROVE) network,
indicate that visibility impairment caused by air pollution occurs
virtually all the time at most federally protected national parks and
wilderness areas, known as Class I areas. The average visual range in
many Class I areas in the western United States is 100 to 150
kilometers, or about one-half to two-thirds of the visual range that
would exist without man-made air pollution.\1\ In most of the eastern
Class I areas of the United States, the average visual range is less
than 30 kilometers, or about one-fifth of the visual range that would
exist under estimated natural conditions. 64 FR 35715 (July 1, 1999).
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\1\ Visual range is the greatest distance, in kilometers or
miles, at which one can view a dark object against the sky.
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B. History of Regional Haze Regulations
In section 169(A)(1) of the 1977 Amendments to the CAA, Congress
established as a national goal the ``prevention of any future, and the
remedying of any existing, impairment of visibility in mandatory class
I Federal areas which impairment results from man-made air pollution.''
Visibility was determined by Congress to be an important value in 156
mandatory Class I Federal areas \2\ as listed in 40 CFR 81.400-437. In
the first phase of visibility protection, EPA promulgated regulations
on December 2, 1980, to address visibility impairment in Class I areas
that is ``reasonably attributable'' to a single source or small group
of sources, i.e., ``reasonably attributable visibility impairment'' or
RAVI. 45 FR 80084. EPA deferred action on regional haze that emanates
from a variety of sources until monitoring, modeling and scientific
knowledge about the relationship between pollutants and visibility
impairment were improved.
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\2\ Areas designated as mandatory Class I Federal areas consist
of national parks exceeding 6000 acres, wilderness areas and
national memorial parks exceeding 5000 acres, and all international
parks that were in existence on August 7, 1977. 42 U.S.C. 7472(a).
In accordance with section 169A of the CAA, EPA, in consultation
with the Department of Interior, promulgated a list of 156 areas
where visibility is identified as an important value. 44 FR 69122
(November 30, 1979). Although states and tribes may designate as
Class I additional areas which they consider to have visibility as
an important value, the requirements of the visibility program set
forth in section 169A of the CAA apply only to ``mandatory Class I
Federal areas.'' Each mandatory Class I Federal area is the
responsibility of a ``Federal Land Manager.'' 42 U.S.C. 7602(i).
When we use the term ``Class I area'' in this action, we mean a
``mandatory Class I Federal area.''
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Congress added section 169B to the CAA in 1990 to conduct
scientific research on regional haze. This legislation established the
Grand Canyon Visibility Transport Commission (GCVTC), which issued its
report, ``Recommendations for Improving Western Vistas,'' on June 10,
1996. These recommendations informed the regulatory development of a
regional haze program, and provided an option for certain western
states to address visibility at 16 Class I areas on the Colorado
Plateau under 40 CFR 51.309.
EPA promulgated a rule to address regional haze on July 1, 1999
known as the Regional Haze Rule (RHR). See 64 FR 35713 as amended at 70
FR 39156 (July 6, 2005) and 71 FR 60631 (October 13, 2006). The RHR
revised the existing visibility regulations to include provisions
addressing regional haze impairment and established a comprehensive
visibility protection program for Class I areas. The requirements for
regional haze, found at 40 CFR 51.308 and 51.309, are included in EPA's
visibility protection regulations at 40 CFR 51.300-309.
The requirement to submit a regional haze SIP revision applies to
all 50 states, the District of Columbia, and the Virgin Islands. States
were required to submit the first SIP addressing regional haze
visibility impairment no later than December 17, 2007. 40 CFR
51.308(b). Since most states, including Nevada, did not submit SIPs
prior to the deadline, EPA made a Finding of Failure to Submit that
under the Clean Air Act had the effect of creating a deadline of
January 15, 2011, for EPA to approve a SIP or publish a Federal
Implementation Plan (FIP). 74 FR 2392 (January 15, 2009). EPA is
publishing this final action to meet this obligation in part.
For a more detailed discussion of the CAA and RHR requirements,
please see sections II and III of our proposal dated June 22, 2011 (76
FR 36450). Our evaluation of the Nevada Regional Haze Plan is in
section IV of the same proposal.
C. Our Proposed Action
On June 22, 2011, EPA proposed to approve all portions of Nevada's
Regional Haze SIP as meeting the relevant requirements of CAA Section
169A and the Regional Haze Rule. We proposed to find that Nevada
appropriately established baseline visibility conditions and a
reasonable progress goal for its one Class I area; developed a long-
term strategy with enforceable measures to ensure reasonable progress
toward achieving the Reasonable Progress Goal in the first planning
period ending in 2018; adequately applied Best Available Retrofit
Technology to specific stationary sources, including RGGS; developed a
regional haze monitoring strategy; provided for periodic progress
reports and revisions; provided for consultation and coordination with
federal land managers; and provided for the regional haze SIP's future
review and revisions. We also proposed to find that emissions from
Nevada do not interfere with other states' measures to protect
visibility as required by CAA Section 110(a)(2)(D)(i)(II). Our proposed
action provides more information about the relevant CAA requirements,
EPA guidance, the State's submittals, and our review and evaluation of
the SIP revisions.
II. BART Determination for NOX at Reid Gardner
We are taking no action in today's rule on the portion of the
Nevada SIP that contains the BART determination at RGGS for
NOX. Following our review of the public comments on this
issue, we performed additional analysis of Nevada's NOX BART
determination for RGGS. As a result, we no longer consider the
currently available information to be sufficient for us to take final
action on the Nevada Division of Environmental Protection's (NDEP's)
determination that rotating overfire air (ROFA) with Rotamix (a form of
selective non-catalytic reduction or SNCR) is the NOX
control technology that represents BART. We intend to consider this
determination in more detail at a future date.
A. Background
The RHR provides that a BART determination must take into account
several factors, which are frequently referred to as the ``five-factor
analysis.'' These factors are listed below (40 CFR
51.308(e)(1)(ii)(A)):
[[Page 17336]]
The cost of compliance for the technically feasible
control technologies;
The energy and non-air quality impacts of the control
technologies;
Any existing air pollution control technologies at the
source;
The remaining useful life of the source; and
The degree of visibility improvement which may reasonably
be anticipated to result from the various control technologies.
B. NDEP's Determination
RGGS consists of four coal-fired boilers, three of which are BART-
eligible units with generating capacity of 100 megawatts (MW) each. A
fourth unit (250 MW) is not BART-eligible. Nevada Energy, the owner of
RGGS, performed a BART analysis for the three BART-eligible RGGS units
and submitted the results of its analysis to NDEP.\3\ In its BART
analysis, Nevada Energy considered several NOX control
technologies and evaluated the cost of compliance and visibility
improvement associated with each technology. In preparing the SIP, NDEP
relied on certain aspects of Nevada Energy's analysis while performing
updated analyses for other aspects. When considering the cost and cost
effectiveness of compliance, NDEP developed its own set of emission
reduction estimates for the various NOX control
technologies, but used Nevada Energy's estimates of total capital and
annual costs.\4\ When considering the degree of visibility improvement
associated with various control technologies, NDEP relied upon the
visibility impacts for each control option as modeled by Nevada Energy,
rather than modeling the visibility impacts attributable to NDEP's own
estimates of NOX removal.
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\3\ Nevada Energy BART Analysis Reports, Reid--Gardner--1--10-
03-08.pdf, Reid--Gardner--2--10-03-08.pdf, Reid--Gardner--3--10-03-
08.pdf. Available in Docket Item No. EPA-R09-OAR-2011-0130-0007.
\4\ Based on a comparison of emission reductions summarized in
Table 1, NDEP Reid Gardner BART Determination, October 22, 2009
(Available as Docket Item No. EPA-R09-OAR-2011-0130-0005), and
emission reductions summarized in Table 3-2 of the NVE BART Analysis
Reports. Visibility impacts as summarized from Table 5-4 of the NVE
BART Analysis Reports.
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In its submittal to NDEP, Nevada Energy determined that low
NOX burners (LNB) with OFA (overfire air) were BART for
NOX. In preparing the SIP, NDEP determined that a more
stringent control technology, ROFA with Rotamix, was BART for
NOX. NDEP eliminated even more stringent control options,
such as Selective Catalytic Reduction (SCR) with LNB and OFA, on the
grounds that ``the $/ton of NOX removed increased
significantly * * * without correspondingly significant improvements in
visibility.'' \5\
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\5\ Revised NDEP Reid Gardner BART Determination Review, page 6.
Available as Docket Item No. EPA-R09-OAR-2011-0130-0005. See also
Nevada Regional Haze SIP, Appendix D (Responses to Comments), pages
D-32 to -42. Available in docket item No. EPA-R09-OAR-2011-0130-003.
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C. Public Comments Relevant to NDEP's Determination
As noted in Section II.B above, NDEP's elimination of control
options more stringent than ROFA with Rotamix was based on the
incremental cost effectiveness ($/ton) and expected visibility
improvement of the various options. EPA received several comments (see
Docket Items 0054, 0057, 0061, 0062 and 0062 Attachment 6) alleging
flaws in NDEP's analysis and response to comments, and stating that SCR
should be BART for NOX at RGGS. These commenters alleged
certain flaws and submitted additional information in criticizing
NDEP's development of the cost effectiveness values and expected
visibility improvement attributable to the more stringent SCR-based
control option.
Regarding cost effectiveness, several commenters (see Docket Items
0054, 0057, 0061, and 0062) alleged that the total capital and annual
cost estimates relied upon by NDEP for the SCR-based control options
were overestimated, included several costs not allowed by EPA's Control
Cost Manual (CCM) such as owner's costs, surcharge, and allowance for
funds used during construction (AFUDC), and used certain variables and
values that were either inflated or unreasonable. One commenter (see
docket item 0062 Attachment 6) performed a revised analysis of SCR cost
effectiveness that adjusted for these alleged issues, and projected a
33 to 40 percent decrease in average and incremental cost effectiveness
values as a result of these adjustments. In addition, commenters stated
that total capital and annual cost estimates lacked evidentiary support
in the administrative record due to the absence of detailed information
such as equipment design parameters, equipment lists, and actual cost
calculations. Finally, commenters also stated that the level of SCR
performance relied upon by NDEP is not supported in the administrative
record by site-specific information such as vendor quotes or
specifications (see Docket Items 0054 and 0061 to 0063).
Regarding visibility improvement, commenters (see Docket Items 0054
and 0062) noted that while baseline visibility modeling indicated that
RGGS currently causes or contributes to visibility impairment at
multiple Class I areas, control scenario visibility modeling results
were only provided for the single closest Class I area, Grand Canyon
National Park. They asserted that the potential visibility benefit at
all affected Class I areas should be accounted for when considering
control technology options. In addition, as described in Section II.B
above, NDEP estimated larger NOX emission reductions than
the emission reductions estimated by Nevada Energy. NDEP, however,
continued to rely on the visibility modeling provided by Nevada Energy,
and did not update the modeling to reflect NDEP's larger NOX
emission reduction estimates. As a result, the existing visibility
modeling does not reflect the incremental visibility improvement
attributable to NDEP's estimates of NOX emission reductions.
Finally, commenters noted that certain modeling files and documentation
were missing from our docket and were unavailable from NDEP, such as
the NOX control scenario modeling result files and
supporting information for NDEP's baseline emission scenarios.
D. EPA's Analysis
After reviewing the public comments, we performed additional
analysis of the cost effectiveness and visibility improvement
associated with the various NOX control technologies
considered by NDEP in determining BART at RGGS. Based upon this
additional analysis, we no longer consider the currently available
supporting information to be sufficiently detailed to allow us to
perform a critical review of these issues. As a result, we are taking
no action in this rule on NDEP's determination that ROFA with Rotamix
is the NOX control technology that represents BART.
Therefore, EPA is taking no action on the portion of the SIP
containing the BART determination for NOX at RGGS including
the corresponding emission limits and schedules of compliance for
NOX at RGGS in the SIP's long-term strategy. Specifically,
these are sections 5.5.3, 5.6.3 and 7.2 of Nevada's SIP that address
the NOX BART control analyses, visibility improvement, and
implementation at RGGS. Since the emissions inventories used to develop
the reasonable progress goal (RPG) did not include NOX
reductions from BART, the fact that we take no action in this rule
regarding the RGGS BART
[[Page 17337]]
determination for NOX does not impact the RPG, and will not
require adjustments to the long-term strategy (LTS) in the SIP.\6\ EPA
will propose further action on this particular portion of the SIP in
the future.
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\6\ Per the Nevada RH SIP, page 6-5, the only BART emission
reductions included in the 2018 emission inventory were
SO2 reductions resulting from presumptive BART limits.
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III. EPA Responses to Public Comments Except BART for NOX at
RGGS
EPA's proposed approval published on June 22, 2011 (76 FR 36450)
included a 30-day public comment period, which ended on July 22, 2011.
We subsequently extended the comment period by 30 days until August 22,
2011 (76 FR 43963). We received comments from WildEarth Guardians, a
consortium of environmental and conservation organizations \7\
(``Consortium''), the Moapa Band of Paiutes, the Nevada Division of
Environmental Protection (NDEP), the National Park Service, the U.S.
Fish and Wildlife Service, and seven individuals. With the exception of
NDEP's comments, which support EPA's proposed approval of its plan,
most of the comments expressed opposition to EPA's full approval of the
SIP. The majority of these comments criticized our proposed approval of
NDEP's determination of BART controls to reduce emissions of
NOX at RGGS. In this final rule approving all other portions
of Nevada's RH SIP, we are responding to all other major comments on
our proposed SIP approval. We find that the SIP is approvable except
BART for NOX at RGGS on which EPA is taking no action.
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\7\ The Consortium's comment letter was signed by
representatives of the Sierra Club, National Parks Conservation
Association, Citizens for Dixie's Future, Defend Our Desert, Friends
of Gold Butte, Grand Canyon Trust, and Western Resource Advocates.
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A. Reasonable Progress Goal
Comments: The National Park Service and U.S. Fish and Wildlife
Service expressed concern that the SIP's reasonable progress analysis
was not consistent with Section 308(d)(1) of the Regional Haze Rule and
EPA's Guidance for Setting Reasonable Progress Goals under the Regional
Haze Program because NDEP ``did not consider what additional emissions
reductions beyond those already being implemented might be reasonable
to improve visibility.'' Similarly, WildEarth Guardians commented that
the Clean Air Act requires EPA to base reasonable progress goals on the
factors set forth under Section 169A(g), and not the bare minimum
required to meet the uniform rate of progress. WildEarth Guardians
expressed concern that ``EPA has overlooked opportunities to further
reduce haze forming pollution from sources in Nevada.'' By contrast,
NDEP asserted that its reasonable progress analysis considered the four
factors required under the Regional Haze Rule (i.e., the costs of
compliance, the time necessary for compliance, the energy and non-air
quality environmental impacts of compliance, and the remaining useful
life of any existing source subject to such requirements).
Specifically, NDEP noted that ``[c]ost was considered first, * * * and
the NDEP concluded it was not necessary to continue with an analysis of
the remaining factors.''
Response: As explained in the proposed rule, in promulgating the
SIP NDEP considered the four factors in setting the reasonable progress
goal for the Jarbidge Wilderness Area, the only Class I area in Nevada.
The RHR and EPA's guidance affords the State considerable flexibility
in determining whether additional emission reduction measures are
needed to achieve the RPG in the first planning period. The NDEP
reasonably concluded that the cost of additional controls was not
warranted given projected emissions reductions from anthropogenic
sources and the fact that the majority of haze at Jarbidge is from
natural and out-of-state sources. Moreover, NDEP noted in its comments
that ``of the five proposed electrical generating units (EGUs) included
in the State's 2018 emissions inventory, only two have moved forward
and are now operational,'' which would further lower emissions
projections for both NOX and SO2 by 2018. The
comments do not demonstrate that the State failed to consider
reasonably the four factors, but the comments question whether the
State should have done a more robust analysis. EPA has considered the
comments and the comments have not provided any further specific facts
that should have been considered in the State's analysis beyond
conclusory criticisms. Therefore, given the broad discretion the RHR
affords the State, and the lack of specificity in the comments on this
issue, EPA reaffirms its proposed decision to approve the State's
reasonable progress goal for Jarbidge.
B. Long-Term Strategy
Comments: The Consortium argued that the SIP ``does not contain
evidence showing full and effective consultation with other states,
does not `ensure that it has included all measures needed to achieve
its apportionment of emission reduction obligations agreed upon'
through that consultation process and further fails to `document the
technical basis, including modeling, monitoring and emissions
information,' on which it relies to determine its apportionment of
emission reduction obligations agreed upon through that process.''
Specifically, the Consortium noted that, ``[a]lthough the Proposed SIP
implies that Nevada consulted with the Western Regional Air Partnership
(``WRAP'') in determining its apportionment of visibility impacts to
Class I areas outside of the State of Nevada, the administrative record
does not support the legally-required level of consultation.'' They
further argued that ``WRAP's failure to apportion Nevada's contribution
does not save Nevada from its independent obligation to require
adequate BART determinations and a long-term strategy to reduce haze-
causing pollutants in out-of-state Class I areas from its pollution
sources.''
Response: EPA disagrees with the assertions that Nevada did not
consult with other states, did not meet its source apportionment
obligations to Class I areas in other states, and did not document the
technical basis for its apportionment as required in 40 CFR
51.308(d)(3)(i), (ii), and (iii). Although Nevada lacked formal
membership in the WRAP, representatives from NDEP actively participated
with other state representatives in the WRAP's committees and work
groups, which jointly directed the development of the WRAP's technical
analyses. Nevada and other western states relied on the WRAP's source
apportionment modeling results to estimate the contribution of out-of-
state emissions and relied on the WRAP's consultation process to ensure
the compatibility of reasonable progress goals and long-term
strategies.\8\ Nevada used the WRAP's source apportionment modeling to
demonstrate the minimal contribution of Nevada's emissions to sulfate
and nitrate extinction at 25 Class I areas in five neighboring
states.\9\ Based on consultation through the WRAP, Nevada identified no
major contributions that supported developing new interstate
strategies, mitigation measures, or emissions reduction obligations.
Nevada and neighboring states agreed that the implementation of BART
and other existing measures in state regional haze plans were
sufficient for the states to meet the reasonable progress goals for
their respective Class I areas, and that future consultation would
address any
[[Page 17338]]
new strategies or measures needed. Moreover, Nevada did not receive any
requests from other states to achieve even greater reductions in its
emissions in order for other states to meet their RPGs. Therefore, EPA
reaffirms its proposed determination that Nevada adequately consulted
with other states, demonstrated that its SIP includes all measures
necessary to obtain its share of emission reductions at other Class I
areas, and provided the technical basis to document its analysis.
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\8\ See 9.1.3 Past Consultation with other States in Nevada's
SIP.
\9\ See 4.3.3 Source Apportionment for Other Class I Areas in
Nevada's SIP.
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C. BART for SO2 and PM10 at RGGS
In addition to extensive comments addressing NDEP's BART
determination for NOX at RGGS, we also received comments
concerning the timing of implementation of BART at RGGS generally, as
well as comments specifically addressing the SO2 and
PM10 BART determinations for RGGS. As noted above, we are
not acting on NDEP's BART determination for NOX at RGGS at
this time. Therefore, our responses concerning RGGS are limited to
comments related to the SO2 and PM10 BART
determinations.
1. BART for SO2 at RGGS
Comments: Regarding NDEP's BART determination for SO2 at
RGGS, WildEarth Guardians expressed concern that ``SO2
limits do not appear to represent the degree of reduction achievable
through the application of the best system of continuous emission
reduction.'' In particular, they asserted that ``it appears that Reid
Gardner is already meeting emission limits that are less than half of
this proposed limit'', and that ``even Nevada recognizes the
SO2 emissions increases will occur as a result of [NDEP's]
proposed BART.'' By contrast, the National Park Service and the U.S.
Fish and Wildlife Service praised ``NDEP's action to lower the
SO2 limit'' at RGGS.
Response: In setting the SO2 BART limits for RGGS, NDEP
took into account the existing controls at the facility, consistent
with CAA Section 169A(g)(2) and 40 CFR 51.308(e)(1)(ii)(A). In
particular, NDEP considered the effect of new fabric filter baghouses
that were installed on all three BART units at RGGS in 2008 and 2009
pursuant to a consent decree between the facility's owner and NDEP and
EPA.\10\ The consent decree established an SO2 emissions
limit of 0.40 lbs/MMbtu (a million British thermal units), based on a
10-day rolling average period, for each of the three BART units.\11\ In
its draft regional haze SIP, NDEP proposed an SO2 emissions
limit of 0.25 lbs/MMbtu for each of the three BART units at RGGS. In
response to comments from EPA and the National Park Service, NDEP
subsequently lowered the BART limits to 0.15 lbs/MMbtu, based on a 24-
hour averaging period.\12\
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\10\ See Nevada's RH SIP Sections 5.5 and 6.5.2.2.
\11\ United States v. Nevada Power Company, Case 2:07-cv-00417
(D. Nev.) (consent decree entered June 15, 2007).
\12\ See Nevada's RH SIP Chapter 5, footnote 4.
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In arguing for further reductions in these BART limits, WildEarth
Guardians notes that, ``according to Clean Air Markets data from the
EPA, units 1-3 are meeting annual sulfur dioxide emission rates of
between 0.054 and 0.064 lbs/MMbtu and have for at least the last two
years.'' However, while the units' current annual average emission
rates may be less than 0.15 lb/MMbtu, these figures are not directly
comparable to the 24-hour rolling average emissions limits set by NDEP
in its BART determination for RGGS. The more relevant points of
comparison are the units' current Title V permit limits of 0.40 lbs/
MMbtu, based on a 10-day rolling average period, which are more than
twice the limit that NDEP has set for each of the three BART units in
its Regional Haze SIP.
In response to commenters' concerns regarding potential increases
in SO2 emissions as a result of NDEP's BART determination at
RGGS, EPA re-examined NDEP's estimates of emission reductions resulting
from BART controls at RGGS. Nevada's SIP provides two sets of estimated
emission reductions resulting from BART controls at RGGS, one based on
the WRAP baseline (4,970 tons) and one based on NDEP's baseline (1,441
tons) for SO2.\13\ Although SO2 emissions are
estimated to increase by 838 tons from NDEP's baseline, they are
expected to decrease by 2,696 tons from the WRAP's baseline. Under both
scenarios, the emissions after BART Controls are held constant at 2,279
tons. Thus, the difference in estimated emissions reductions is a
reflection of the large difference between the WRAP baseline and the
NDEP baseline for SO2.
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\13\ See Nevada's RH SIP, Table 5-6 Reid Gardner: BART Emissions
Reductions in Tons per Year.
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NDEP's baseline emissions for SO2 were calculated using
acid rain data that omitted data deemed invalid due to monitoring
problems that were addressed by the consent decree. According to NDEP,
the omission of the invalid data effectively lowered the baseline
emissions (measured in lbs/MMbtu) by nearly half.\14\ Thus, the
projected increase in SO2 appears to be an artifact of
NDEP's exceptionally low baseline that is attributable to the exclusion
of invalid data.
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\14\ See Nevada's RH SIP Section 5.5.
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From a broader perspective, NDEP's BART determination for
SO2 at RGGS will result in a lower emissions limit (0.15
lbs/MMbtu based on a 24-hour rolling average compared to the current
Title V Permit limit of 0.40 lbs/MMbtu based on a 10-day rolling
average period) related to the new fabric filter baghouses and existing
wet soda ash with a dry flue gas desulfurization system. Since the BART
determination lowers the short-term emissions limit, there is no valid
reason to suspect that SO2 emissions will increase as a
result of BART controls. EPA will use the progress report due five
years after the SIP's approval to evaluate actual SO2
emissions at RGGS to ensure that NDEP's BART determination has not
resulted in increased emissions and will encourage NDEP to take
appropriate action, if necessary, at that time.
2. BART for PM10 at RGGS
Comments: Regarding the PM10 limit, WildEarth Guardians
expressed concern that ``the proposed BART determination is
unenforceable because there are no monitoring, recordkeeping, or
reporting requirements proposed that would ensure compliance with the
24-hour limits. There are simply no monitoring requirements proposed
that would actually ensure that the PM limit is met on a continuous
basis. This is contrary to the Clean Air Act, which defines BART based
on continuous emission reductions.''
Response: As explained in EPA's BART Guidelines, ``[m]onitoring
requirements generally applicable to sources, including those that are
subject to BART, are governed by other regulations. See, e.g., 40 CFR
part 64 (compliance assurance monitoring); 40 CFR 70.6(a)(3) (periodic
monitoring); 40 CFR 70.6(c)(1) (sufficiency monitoring).'' \15\ The
monitoring, recordkeeping and reporting requirements specifically
applicable to RGGS are found in the existing Nevada SIP as well as the
facility's Title V permit. In particular, the applicable SIP requires
continuous monitoring of opacity and compliance with a 20 percent
opacity limit.\16\ Although opacity does not directly correlate with
particulate concentrations, it is a good indicator of proper operation
of the baghouse since almost any opacity from a baghouse-controlled
coal-fired boiler
[[Page 17339]]
is indicative of leaks in the baghouse. Under Part 64, such an
excursion or exceedance must be addressed ``as expeditiously as
practicable in accordance with good air pollution control practices for
minimizing emissions.'' \17\ For directly assuring compliance with
existing PM10 limits, the Title V permit for RGGS contains
an annual stack test requirement using Method 5 for PM and Method 201A/
202 for PM10. Given the current opacity limit in the SIP and
the compliance methods in RGGS's Title V permit, we are approving the
BART determination for PM10 in Nevada's RH SIP. We will
continue to work with Nevada to ensure that all appropriate compliance
provisions are in the SIP.
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\15\ 40 CFR part 51 Appendix Y, Section V.
\16\ See 40 CFR 52.1470(c); Nevada Administrative Code 445B.256-
267, 22017.
\17\ 40 CFR 64.7(d)(1).
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3. Timing of Implementation
Comments: WildEarth Guardians expressed concern that ``EPA has not
demonstrated that `by January 1, 2015' is as expeditiously as practical
for complying with BART at Reid Gardner, nor shown that it is
reasonable to allow the facility a full five years to come into
compliance with BART.''
Response: The Nevada BART regulation in the Regional Haze SIP
requires that the BART control measures at RGGS must be installed and
operating ``[o]n or before January 1, 2015; or (2) [n]ot later than 5
years after approval of Nevada's state implementation plan for regional
haze by the United States Environmental Protection Agency Region 9,
whichever occurs first.'' Given the date of our approval of Nevada's
SIP, the BART implementation deadline for the RGGS is January 1, 2015,
about three years from the date of this final rule. EPA considers
Nevada's choice of the January 1, 2015, to be reasonable in this
instance.
D. Corrections to EPA's Technical Analysis
Comments: NDEP noted a few corrections to EPA's analysis in the
proposed rule at 76 FR 36450 (June 22, 2011), but stated that these
minor corrections do not alter any of EPA's conclusions. The first
correction was to note that the percentages of emissions by source
category shown in section IV.C.2 of EPA's proposed rule are based on
the 2018 emissions inventory. The proposal omitted the date of the
inventory. Secondly, NDEP commented that the discussion of predominant
sources of PM2.5 was in error because ``the predominant
source of PM fine emissions are windblown dust (43 percent) and
fugitive dust (30 percent).'' EPA had mistakenly attributed PM fine
emissions to natural fires (49 percent) and area sources (37 percent).
Lastly, NDEP commented on the sources of visibility impairment, saying
that soil in PM2.5 is mostly from windblown dust, not
natural fire. EPA had mistakenly attributed the source of
PM2.5 to natural fire.
Response: EPA is correcting the record as noted above.
IV. EPA Action
Under section 110(k)(3) of the CAA, EPA is fully approving most
portions of the Nevada Regional Haze SIP as satisfying all of the
relevant requirements of CAA Section 169A and the Regional Haze Rule.
For the portions of the SIP establishing BART for NOX at
RGGS, EPA is taking no action at this time, and will take action on
those portions of the SIP in a separate rulemaking.
We find that Nevada has met the following Regional Haze Rule
requirements: The State established baseline visibility conditions and
reasonable progress goals for each of its Class I areas; the State
developed a long-term strategy with enforceable measures ensuring
reasonable progress towards meeting the reasonable progress goals for
the first ten-year planning period, through 2018; the State has
adequately addressed the application of Best Available Retrofit
Technology to specific stationary sources, except for NOX at
RGGS; the State has an adequate regional haze monitoring strategy; the
State provided for consultation and coordination with federal land
managers in producing its regional haze plan; and, the State provided
for the regional haze plan's future revisions.
In addition, under section 110(k)(3) of the CAA, we are fully
approving the Nevada Regional Haze SIP as satisfying the CAA Section
110(a)(2)(D)(i)(II) requirement to prohibit emissions that will
interfere with measures to protect visibility in another state for the
1997 8-hour ozone and 1997 PM2.5 NAAQS.\18\
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\18\ As noted in our proposal, 76 FR 36465, we previously
approved Nevada's SIP for Interstate Transport as meeting the other
requirements of CAA section 110(a)(2)(D)(i) for the 1997 8-hour
ozone and 1997 PM2.5 NAAQS. See 70 FR 41629. We are now
codifying this prior approval along with our current approval under
a new section entitled ``Interstate Transport.''
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V. Statutory and Executive Order Reviews
Under the Clean Air Act, the Administrator is required to approve a
SIP submission that complies with the provisions of the Act 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 Clean Air Act.
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 Clean Air Act; and
Does not interfere with Executive Order 12898 (59 FR 7629
(Feb. 16, 1994)) because EPA lacks the discretionary authority to
address environmental justice in this rulemaking.
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. However, the Moapa Band of
Paiutes did raise issues in the context of the BART determination for
RGGS, which will be addressed at a future date. Region 9 engaged in
formal consultation with the Moapa Band of Paiutes on August 11, 2011,
and heard these issues in person. We will continue to consult with
Moapa on RGGS.
[[Page 17340]]
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 Clean Air Act, petitions for
judicial review of this action must be filed in the United States Court
of Appeals for the appropriate circuit by May 25, 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 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, Nitrogen oxides, Sulfur
dioxide, Particulate matter, Reporting and recordkeeping requirements,
Visibility, Volatile organic compounds.
Dated: December 13, 2011.
Jared Blumenfeld,
Regional Administrator, Region 9.
Part 52, chapter I, title 40 of the Code of Federal Regulations 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 DD--Nevada
0
2. In Sec. 52.1470(c):
0
a. In paragraph (c), Table 1 is amended by adding an entry for
``445B.029'' after the entry for ``445B.022'', and adding entries for
``445B.22095,'' and ``445B.22096'' after the entry for ``445B.22093''.
0
3. The table in paragraph (e) is amended by adding an entry for
``Nevada Regional Haze State Implementation Plan (October 2009)'' to
the end of the table.
Sec. 52.1470 Identification of plan.
* * * * *
(c) * * *
Table 1--EPA-Approved Nevada Regulations
----------------------------------------------------------------------------------------------------------------
State Additional
State citation Title/subject effective date EPA approval date explanation
----------------------------------------------------------------------------------------------------------------
Nevada Administrative Code, Chapter 445B, Air Controls, Air Pollution; Nevada Administrative Code, Chapter 445,
Air Controls, Air Pollution; Nevada Air Quality Regulations--Definitions
����������������������������������������������������������������������������������������������������������������
* * * * * * *
445B.029......................... ``Best available 4/23/09 [Insert page number Included in
retrofit where the document supplemental SIP
technology'' begins 3/26/12]. revision submitted
defined. on September 20,
2011, and approved
as part of
approval of Nevada
Regional Haze SIP.
* * * * * * *
445B.22095....................... Emission limitation 4/23/09 [Insert page number Included in
for BART. where the document supplemental SIP
begins 3/26/12]. revision submitted
on September 20,
2011, and approved
as part of
approval of Nevada
Regional Haze SIP.
445B.22096, excluding the NOX Control measures 1/28/10 [Insert page number Included in
emission limits and control constituting BART; where the document supplemental SIP
types in sub-paragraph (1)(c). limitations on begins 3/26/12]. revision submitted
emissions. on September 20,
2011, and approved
as part of
approval of Nevada
Regional Haze SIP.
Excluding the NOX
emission limits
and control types
for units 1, 2 and
3 of NV Energy's
Reid Gardner
Generating
Station.
* * * * * * *
----------------------------------------------------------------------------------------------------------------
* * * * *
(e) * * *
[[Page 17341]]
----------------------------------------------------------------------------------------------------------------
Applicable
Name of SIP provision geographic or State EPA approval date Explanation
nonattainment area submittal date
----------------------------------------------------------------------------------------------------------------
* * * * * * *
Nevada Regional Haze State State-wide......... 11/18/09 [Insert page number Excluding Appendix
Implementation Plan (October where the document A (``Nevada BART
2009), excluding the BART begins 3/26/12]. Regulation''). The
determination and the associated Nevada BART
emission limits for NOX at Reid regulation,
Gardner Generating Station in including NAC
sections 5.5.3, 5.6.3 and 7.2. 445B.029,
445B.22095, and
445B.22096, is
listed above in 40
CFR 52.1470(c).
* * * * * * *
----------------------------------------------------------------------------------------------------------------
0
3. Section 52.1488 is amended by adding paragraph (e) to read as
follows:
Sec. 52.1488 Visibility protection.
* * * * *
(e) Approval. On November 18, 2009, the Nevada Division of
Environmental Protection submitted the ``Nevada Regional Haze State
Implementation Plan.'' With the exception of the BART determination and
the associated emission limits for NOX at Reid Gardner
Generating Station in sections 5.5.3, 5.6.3 and 7.2, the Nevada
Regional Haze State Implementation Plan, as supplemented and amended on
February 18, 2010 and September 20, 2011, meets the applicable
requirements of Clean Air Act sections 169A and 169B and the Regional
Haze Rule in 40 CFR 51.308.
0
4. Add a new Sec. 52.1491 to read as follows:
Sec. 52.1491 Interstate transport.
(a) Approval. On February 7, 2007, the Nevada Division of
Environmental Protection submitted the ``Nevada State Implementation
Plan for Interstate Transport to Satisfy the Requirements of the Clean
Air Act 110(a)(2)(D)(i) for the 8-hour Ozone and PM2.5 NAAQS
Promulgated in July 1997'' (``2007 Interstate Transport SIP''). The
2007 Interstate Transport SIP meets the requirements of Clean Air Act
section 110(a)(2)(D)(i) for the 1997 8-hour ozone and 1997
PM2.5 NAAQS other than the requirements of Clean Air Act
section 110(a)(2)(D)(i)(II) regarding interference with other states'
measures to protect visibility.
(b) Approval. The requirements of Clean Air Act section
110(a)(2)(D)(i)(II) regarding interference with other states' measures
to protect visibility for the 1997 8-hour ozone and 1997
PM2.5 NAAQS are met by the ``Nevada Regional Haze State
Implementation Plan,'' as supplemented and amended on February 18, 2010
and September 20, 2011.
[FR Doc. 2012-7025 Filed 3-23-12; 8:45 am]
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