Implementation of the New Source Review (NSR) Program for Particulate Matter Less Than 2.5 Micrometers (PM2.5, 28646-28661 [2011-12089]
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28646
Federal Register / Vol. 76, No. 96 / Wednesday, May 18, 2011 / Rules and Regulations
If
you have questions on this rule, call or
e-mail Kay Wade, Bridge
Administration Branch, Coast Guard;
telephone 504–671–2128, e-mail
Kay.B.Wade@uscg.mil. If you have
questions on viewing the docket, call
Renee V. Wright, Program Manager,
Docket Operations, telephone 202–366–
9826.
FOR FURTHER INFORMATION CONTACT:
The Union
Pacific Railroad has requested a
temporary deviation from the operating
schedule for the swing span bridge
across the Calcasieu River, mile 36.4, at
Westlake, Calcasieu Parish, Louisiana.
The swing span bridge has a vertical
clearance of 1.07 feet above mean high
water, elevation 3.56 feet Mean Gulf
Level in the closed-to-navigation
position.
In accordance with 33 CFR 117.5, the
bridge currently opens on signal for the
passage of vessels. This deviation allows
the swing span of the bridge to remain
closed to navigation from 8 a.m. through
5 p.m. with an opening for the passage
of vessels from 12 noon to 1 p.m. on the
following Thursdays: June 2, 9, 16, 23,
and 30, 2011.
The closures are necessary in order to
remove and install the structural steel,
new gear motors, and shafts at both ends
of the bridge and the center pivot pier.
This maintenance is essential for the
continued operation of the bridge.
Notices will be published in the Eighth
Coast Guard District Local Notice to
Mariners and will be broadcast via the
Coast Guard Broadcast Notice to
Mariners System.
Navigation on the waterway is
minimal at the bridge site. The very
limited commercial traffic at the bridge
site consists of commercial tugs with
tows. There are only two companies that
transit above the bridge. The bridge will
be able to open for emergencies if
necessary. There are no alternate
waterway routes available. Based on
experience and coordination with
waterway users, it has been determined
that these closures will not have a
significant effect on vessels that use the
waterway.
In accordance with 33 CFR 117.35(e),
the drawbridge must return to its regular
operating schedule immediately at the
end of the designated time period. This
deviation from the operating regulations
is authorized under 33 CFR 117.35.
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SUPPLEMENTARY INFORMATION:
Dated: May 9, 2011.
David M. Frank,
Bridge Administrator.
[FR Doc. 2011–12246 Filed 5–17–11; 8:45 am]
BILLING CODE 9110–04–P
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[EPA–HQ–OAR–2003–0062: FRL–9306–9]
Friday, excluding legal holidays. The
telephone number for the Public
Reading Room is (202) 566–1744, and
the telephone number for the Air Docket
is (202) 566–1742.
RIN 2060–AP75
FOR FURTHER INFORMATION CONTACT:
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
Implementation of the New Source
Review (NSR) Program for Particulate
Matter Less Than 2.5 Micrometers
(PM2.5); Final Rule To Repeal
Grandfather Provision
Environmental Protection
Agency (EPA).
ACTION: Final rule.
Mr. Dan deRoeck, Air Quality Policy
Division, (C504–03), U.S.
Environmental Protection Agency,
Research Triangle Park, NC, 27711;
telephone number (919) 541–5593; fax
number (919) 541–5509; or e-mail
address: deroeck.dan@epa.gov.
SUPPLEMENTARY INFORMATION:
AGENCY:
The EPA is issuing a final rule
that repeals the ‘‘grandfather’’ provision
for particulate matter less than 2.5
micrometers (PM2.5) under the Federal
Prevention of Significant Deterioration
(PSD) permit program, which is
administered by EPA in states that lack
a PSD permit program in their approved
state implementation plan (SIP). The
grandfather provision allowed certain
facilities under certain circumstances to
satisfy the PSD permit program
requirements for PM2.5 by meeting the
requirements for controlling particulate
matter less than 10 micrometers (PM10)
and analyzing impacts on PM10 air
quality as a surrogate approach based on
an EPA policy known as the ‘‘1997 PM10
Surrogate Policy.’’ In its February 11,
2010, notice of proposed rulemaking,
EPA also proposed to end early the 1997
PM10 Surrogate Policy in EPA-approved
state PSD programs during the
remainder of the SIP development
period, which ends on May 16, 2011.
EPA is taking no final action on that
aspect of the proposal.
DATES: This final rule is effective on July
18, 2011.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. EPA–HQ–OAR–2003–0062. All
documents in the docket are listed on
the https://www.regulations.gov Web
site. Although listed in the index, some
information may not be publicly
available, e.g., Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically through
https://www.regulations.gov or in hard
copy at the Air Docket, EPA/DC, EPA
West, Room 3334, 1301 Constitution
Avenue, Northwest, Washington, DC.
The Public Reading Room is open from
8:30 a.m. to 4:30 p.m., Monday through
SUMMARY:
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The
information in this Supplementary
Information section of this preamble is
organized as follows:
I. General Information
A. Does this action apply to me?
B. Where can I get a copy of this document
and other related information?
II. Overview of This Final Rule
III. Background
A. Prevention of Significant Deterioration
Program
B. Fine PM and the NAAQS for PM2.5
C. How is the PSD program for PM2.5
implemented?
IV. Grandfather Provision for PM2.5 in the
Federal PSD Program
A. What is the grandfather provision for
PM2.5?
B. Why did EPA propose to repeal the
grandfather provision for PM2.5?
C. Summary of Comments and Responses
on the Proposed Repeal of the
Grandfather Provision
D. What final action is EPA taking on the
grandfather provision for PM2.5?
V. What action is EPA taking on the 1997
PM10 Surrogate Policy for state PSD
programs?
VI. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations
K. Congressional Review Act
L. Conclusion and Determination Under
Section 307(d)
VII. Judicial Review
VIII. Statutory Authority
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Federal Register / Vol. 76, No. 96 / Wednesday, May 18, 2011 / Rules and Regulations
I. General Information
A. Does this action apply to me?
Entities potentially affected by this
action include those proposed new and
modified major stationary sources
subject to the Federal PSD program that
submitted a complete application for a
PSD permit before the July 15, 2008,
effective date of the final PM2.5 New
Source Review (NSR) Implementation
Rule (73 FR 28321), but have not yet
received a final and effective permit
authorizing the source to commence
construction.
The EPA estimates that fewer than 30
proposed new major sources or
modifications will be affected by the
repeal of the grandfather provision in
the Federal PSD program. At least two
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projects known to have been
grandfathered received final permits to
construct (that are effective) prior to
EPA taking action to stay the provision
in June 2009; EPA’s final action to
repeal the grandfather provision does
not apply retroactively to such permits.
The majority of sources potentially
affected are expected to be in the
following groups:
Industry group
NAICS a
Electric services ........................................................................................
Petroleum refining ....................................................................................
Industrial inorganic chemicals ..................................................................
Industrial organic chemicals .....................................................................
Miscellaneous chemical products .............................................................
Natural gas liquids ....................................................................................
Natural gas transport ................................................................................
Pulp and paper mills .................................................................................
Paper mills ................................................................................................
Automobile manufacturing ........................................................................
221111, 221112, 221113, 221119, 221121, 221122.
32411.
325181, 32512, 325131, 325182, 211112, 325998, 331311, 325188.
32511, 325132, 325192, 325188, 325193, 32512, 325199.
32552, 32592, 32591, 325182, 32551.
211112.
48621, 22121.
32211, 322121, 322122, 32213.
322121, 322122.
336111, 336112, 336712, 336211, 336992, 336322, 336312, 33633,
33634, 33635, 336399, 336212, 336213.
325411, 325412, 325413, 325414.
Pharmaceuticals .......................................................................................
a North
American Industry Classification System.
Entities affected by this action also
include state and local governments
responsible for implementing PSD preconstruction permit programs for new
and modified major stationary sources
under the Federal PSD permit program
(40 CFR 52.21).
B. Where can I get a copy of this
document and other related
information?
In addition to being available in the
docket, an electronic copy of this final
rule will also be available on the World
Wide Web. Following signature by the
EPA Administrator, a copy of this final
rule will be posted in the regulations
and standards section of our NSR home
page located at https://www.epa.gov/nsr.
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II. Overview of This Final Rule
In this final rule we 1 are taking final
action on one of the two actions that we
proposed in a notice of proposed
rulemaking on February 11, 2010, at
75 FR 6827. We are taking final action
on the proposal to repeal the
grandfather provision for PM2.5
contained in the Federal PSD rules at 40
CFR 52.21(i)(1)(xi). The grandfather
provision, applicable only to PSD
source applications that were
determined to be complete before July
15, 2008, enabled those applications to
continue to be reviewed for PM10 (i.e.,
the 1997 PM10 Surrogate Policy) in lieu
of the new requirements for PM2.5,
1 In this preamble, the terms ‘‘we,’’ ‘‘us,’’ and ‘‘our’’
refer to the EPA.
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which became effective on July 15,
2008.
When EPA issued the PM10 Surrogate
Policy in 1997, the policy enabled
sources, EPA, and state and local
permitting authorities to address the
PSD requirements for PM2.5 simply by
satisfying the requirements for PM10—a
regulated form of particulate matter
(PM) that includes PM2.5 as well as
larger particles. As explained in the
1997 PM10 Surrogate Policy, some
alternative to directly addressing PM2.5
was necessary at that time because of
various technical problems that made it
infeasible to estimate PM2.5 and conduct
the analyses necessary to demonstrate
compliance with the applicable PM2.5
requirements under the PSD program as
required by section 165 of the Clean Air
Act (CAA or Act).
More recently, EPA has made
important progress in addressing the
technical issues that impeded a PM2.5
analysis. With the deployment and
operation of the monitoring network for
PM2.5 beginning in 1999, ambient air
quality monitoring data has become
more abundantly available. Also, EPA
has promulgated screening tools,
including a significant emissions rate
(SER), significant impact levels (SILs),
and a significant monitoring
concentration (SMC) to streamline the
implementation of the PSD program for
PM2.5. Finally, EPA has issued revised
test methods for sampling emissions of
PM2.5 and its condensable fraction, and
issued interim modeling guidance for
modeling PM2.5 emissions to complete a
cumulative air quality analysis for
PM2.5.
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Accordingly, in this final action, EPA
will end the use of the 1997 PM10
Surrogate Policy for PSD permits under
the Federal PSD program (40 CFR 52.21)
for sources that have been covered by
the grandfather provision (that is, those
sources for which a complete permit
application was submitted before July
15, 2008 2) and that have not yet been
issued a permit by the effective date of
this final rule. After this final rule
becomes effective, in order for those
permits to be issued, such applications
will have to be reviewed directly against
the PM2.5 requirements or, alternatively,
use a surrogate approach for PM2.5
(other than the 1997 PM10 Surrogate
Policy) that is consistent with the
applicable case law. Thus, those
affected PSD permit applications must
be amended to include further analyses
to demonstrate compliance with the
PSD requirements for PM2.5.
Alternatively, those affected PSD permit
applications must show that PM10 is an
adequate surrogate for PM2.5 for that
specific project. The demonstration
must show, at a minimum, that the
source’s emissions are controlled to a
level that satisfies Best Available
Control Technology (BACT)
requirements for PM2.5 and that the
emissions will not cause or contribute to
a violation of any National Ambient Air
Quality Standard (NAAQS or standard)
for PM2.5.
2 Sources that applied for a PSD permit under the
Federal PSD program on or after July 15, 2008, are
already excluded from using the 1997 PM10
Surrogate Policy as a means of satisfying the PSD
requirements for PM2.5. See 73 FR 28321.
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Federal Register / Vol. 76, No. 96 / Wednesday, May 18, 2011 / Rules and Regulations
We believe that it is appropriate to
terminate the use of the 1997 PM10
Surrogate Policy at this time for those
PSD applications grandfathered under
the Federal PSD program because the
necessary technical tools to conduct
PM2.5 analyses for PSD sources are now
available. The 1997 PM10 Surrogate
Policy was always intended as an
interim measure that was to remain in
effect only as long as needed. Over the
past 13 years, EPA believes that the
necessary technical tools and test
methods required to show compliance
with PM2.5 have been developed and,
hence, we believe that the need for this
interim approach no longer exists.
We do not believe that the use of the
1997 PM10 Surrogate Policy affords the
same degree of protection of the PM2.5
NAAQS from major new and modified
stationary sources as does the direct
analysis of PM2.5 emissions. In addition
to the fact that the original PM2.5
NAAQS promulgated in 1997 were
generally more stringent than the
corresponding PM10 NAAQS, the
strengthening of the 24-hour primary
PM2.5 NAAQS in 2005 created a greater
disparity between the relative
stringency of the PM2.5 and PM10
standards. Thus, now that the necessary
technical tools are available, we believe
that it is important to move as quickly
as possible to implement fully the PSD
program for PM2.5.
We recognize that this action will in
some cases increase the PSD permit
review timeframe (although not
unexpectedly) for the affected
grandfathered sources, but we believe
that the use of the 1997 PM10 Surrogate
Policy should be permanently
discontinued under the Federal PSD
program. Those grandfathered sources
with pending permits have been on
notice since June 1, 2009, (the date of
our Federal Register notice announcing
that we had agreed to reconsider the
grandfather provision and to
administratively stay the provision so
that we could propose repealing it) that
EPA was considering ending the
grandfather provision for PM2.5 and, as
noted above, now have additional
technical tools to complete the
permitting process for PM2.5.
In our February 2010 proposed rule,
we also proposed to end the use of the
1997 PM10 Surrogate Policy for permits
issued under PSD programs
implemented by states as part of their
approved SIP. We received and have
reviewed some comments that support
an early end to the policy and some
comments that oppose ending the policy
earlier than the original May 16, 2011,
sunset date. Some of the opposing
comments also asked EPA to extend the
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time that the policy could be used
beyond the original sunset date. At this
time, however, we are taking no action
on our proposal to end the use of the
1997 PM10 Surrogate Policy or to
otherwise change the time period during
which the policy could continue to be
used.
Thus, as announced in the May 2008
rulemaking, the 1997 PM10 Surrogate
Policy may not be used for any state
PSD permits after the 3 years allowed
for SIP development (ending May 16,
2011). With the end of the 1997 PM10
Surrogate Policy in SIP-approved states
on May 16, 2011, and the repeal of the
grandfather provision in this final
action, the 1997 PM10 Surrogate Policy
may not be relied on for any pending or
future applications.
III. Background
A. Prevention of Significant
Deterioration Program
The NSR provisions of the Act are a
combination of air quality planning and
air pollution control technology
program requirements for new and
modified major stationary sources of air
pollution. Section 109 of the Act
requires EPA to promulgate primary
NAAQS to protect public health and
secondary NAAQS to protect public
welfare. Once we have set these
standards, states must develop, adopt,
and submit to us for approval SIPs that
contain emission limitations and other
control measures to attain and maintain
the NAAQS and to meet the other
requirements of section 110(a) of the
Act.
Part C of title I of the Act contains the
requirements for a component of the
major NSR program known as the PSD
(short for ‘‘Prevention of Significant
Deterioration’’) program. The PSD
program sets forth procedures for the
preconstruction review and permitting
of new and modified major stationary
sources of air pollution locating in areas
meeting the NAAQS (‘‘attainment’’
areas) and areas for which there is
insufficient information to classify an
area as either attainment or
nonattainment (‘‘unclassifiable’’ areas).
In most states, EPA has approved a PSD
permit program that is part of the
applicable SIP. The Federal PSD
program at 40 CFR 52.21 applies in
states that lack a SIP-approved PSD
permit program, and in Indian country.3
3 We have delegated our authority to some states
that lack an approved PSD program in their SIPs
and have requested the authority to implement the
Federal PSD program. The EPA remains the
reviewing authority in non-delegated states lacking
SIP-approved programs. The current status of
individual state PSD programs can be found at
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The applicability of the PSD program to
a new major stationary source or major
modification must be determined in
advance of construction and is a
pollutant-specific determination. Once a
major new source or major modification
is determined to be subject to the PSD
program (i.e., to be a ‘‘PSD source’’),
among other requirements, it must
undertake a series of analyses for each
regulated NSR pollutant subject to
review to demonstrate that it will use
the BACT and will not cause or
contribute to a violation of any NAAQS
or increment. In cases where the
source’s emissions of any NSR regulated
pollutant may adversely affect an area
specially classified as ‘‘Class I,’’ such as
national parks and wilderness areas,
additional review must be conducted to
protect the Class I area’s increments and
special attributes referred to as ‘‘air
quality related values.’’
When the reviewing authority reaches
a preliminary decision to authorize
construction of a proposed major new
source or major modification, the
authority must provide notice of the
preliminary decision and an
opportunity for comment by the general
public, industry, and other persons that
may be affected by the emissions of the
proposed major source or major
modification. After considering these
comments, the reviewing authority
issues a final determination on the
construction permit in accordance with
the PSD regulations. However, under
EPA regulations at 40 CFR part 124 and
similar state regulations, an
administrative appeal of a permitting
determination may prevent the permit
from becoming final and effective until
the appeal is resolved.
B. Fine PM and the NAAQS for PM2.5
Fine particles in the atmosphere are
made up of a complex mixture of
components. Common constituents
include sulfates; nitrates; ammonium;
elemental carbon; a great variety of
organic compounds; and inorganic
material (including metals, dust, sea
salt, and other trace elements) generally
referred to as ‘‘crustal’’ material,
although it may contain material from
other sources. Airborne PM with a
nominal aerodynamic diameter of 2.5
micrometers or less (a micrometer is
one-millionth of a meter, and 2.5
micrometers is less than one-seventh the
average width of a human hair) is
considered to be ‘‘fine particles,’’ and is
also known as PM2.5. ‘‘Primary’’ particles
are emitted directly into the air as solid
or liquid particles (e.g., elemental
EPA’s Web site at https://www.epa.gov/nsr/
where.html.
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Surrogate Policy was designed to
temporarily help states implement the
CAA requirements for PSD pertaining to
the new PM2.5 NAAQS and PM2.5 as a
regulated pollutant. We intended to
make the policy available until we
resolved the known technical
difficulties associated with addressing
PM2.5.5
We believed the 1997 PM10 Surrogate
Policy was necessary because section
165(a)(1) of the Act provides that no
new or modified major source may be
constructed without a PSD permit that
meets all of the section 165(a)
requirements with respect to the
regulated pollutant. Moreover, section
165(a)(3) provides that the emissions
from any such source may not cause or
contribute to a violation of ‘‘any
NAAQS.’’ The EPA policy for
implementing the Federal PSD program
provides that the term ‘‘any NAAQS’’
applies to any existing NAAQS,
including new or revised NAAQS upon
their effective date. Also, section
165(a)(4) requires BACT for each
pollutant subject to PSD regulation.
PM2.5 became a regulated pollutant
when EPA promulgated the NAAQS for
PM2.5 in 1997.
On November 1, 2005, we proposed
the Clean Air Fine Particle
Implementation Rule (PM2.5
Implementation Rule) to implement the
1997 PM2.5 NAAQS. See 70 FR 65984.
The PM2.5 Implementation Rule
proposal described the requirements
that states and tribes must meet in their
implementation plans for attainment of
the PM2.5 NAAQS. Among other things,
that rule proposal sought comments on
revisions to the NSR program in
attainment and unclassifiable areas (the
PSD program), and in nonattainment
areas (the nonattainment NSR program).
For PSD, EPA proposed to revise the
existing PSD rules in several ways: by
C. How is the PSD program for PM2.5
proposing a PSD major source threshold
implemented?
and SER for PM2.5; proposing to define
After we promulgated the NAAQS for applicable precursors to regulate under
PM2.5 in 1997, we issued a guidance
PSD and SERs for those precursors;
document titled, ‘‘Interim
proposing to clarify that condensable
Implementation for the New Source
PM2.5 must be included in determining
Review Requirements for PM2.5’’ (John S. major source status; proposing options
4 That
Seitz, EPA, October 23, 1997).
for implementing the preconstruction
guidance document, referred to
monitoring requirements for PM2.5; and
throughout this preamble as the ‘‘1997
proposing transition provisions for
PM10 Surrogate Policy,’’ allows proposed implementing the new PSD
major sources and major modifications
requirements for PM2.5.
to satisfy the PSD requirements for
On September 21, 2007, EPA
PM2.5 by meeting the requirements for
proposed additional program elements
controlling PM10 and for analyzing
for the PSD program for PM2.5 that were
impacts on PM10 air quality as a
surrogate approach. The 1997 PM10
5 We identified various technical difficulties,
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carbon from diesel engines or fire
activities, or condensable organic
particles from gasoline engines).
‘‘Secondary’’ particles (e.g., sulfates and
nitrates) form in the atmosphere as a
result of various chemical reactions.
The health effects associated with
exposure to PM2.5 are significant and
well studied. Epidemiological studies
have shown a significant correlation
between elevated PM2.5 levels and
premature mortality. Other important
effects associated with PM2.5 exposure
include aggravation of respiratory and
cardiovascular disease (as indicated by
increased hospital admissions,
emergency room visits, absences from
school or work, and restricted activity
days), lung disease, decreased lung
function, asthma attacks, and certain
cardiovascular problems. Individuals
particularly sensitive to PM2.5 exposure
include older adults, people with heart
and lung disease, and children.
The EPA has established primary
health-based long-term and short-term
NAAQS for PM2.5. The long-term annual
average standard is 15 micrograms per
cubic meter (μg/m3), established in
1997. See 62 FR 38652. The short-term
24-hour standard is 35 μg/m3,
established in 2006. See 71 FR 61286.
At the time we established the primary
standards in 1997, we also established
welfare-based (secondary) standards
identical to the primary standards. The
secondary standards are designed to
protect against major environmental
effects of PM2.5 such as visibility
impairment, soiling, and materials
damage.
In addition, EPA has established a
short-term primary and secondary
NAAQS for PM10 as an indicator for
coarse PM. The short-term standard for
PM10 is 150 μg/m3. See 71 FR 61236.
4 Available
in the docket for this rulemaking, ID
No. EPA–HQ–OAR–2003–0062, and at https://
www.epa.gov/region07/programs/artd/air/nsr/
nsrmemos/pm25.pdf.
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including the lack of necessary tools to calculate the
emissions of PM2.5 and related precursors, the lack
of adequate modeling techniques to project ambient
impacts, the lack of PM2.5 monitoring sites, and the
lack of adequate approved test methods.
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not included in the 2005 PM2.5
Implementation Rule proposal. The
2007 PSD proposal included several
options for defining the PM2.5
increments, SILs, and an SMC for PM2.5.
Increments define maximum allowable
increases in pollutant concentrations
above a baseline concentration for a
particular area. The SILs and SMC are
useful screening tools for effectively
implementing the air quality impact
requirements under PSD. See 72 FR
54112.
On May 16, 2008, EPA published a
final PM2.5 NSR Implementation Rule to
complete the rulemaking for NSR based
on the 2005 PM2.5 Implementation Rule
proposal. The 2008 PM2.5 NSR
Implementation Rule contains
requirements for state and tribal plans to
implement the Act’s preconstruction
review provisions for the PM2.5 NAAQS
in both attainment and nonattainment
areas. See 73 FR 28321. The 2008 PM2.5
NSR Implementation Rule generally
requires that, as of the effective date of
the new rule (July 15, 2008), major
stationary sources seeking permits must
begin directly satisfying the PM2.5
requirements, rather than relying on the
1997 PM10 Surrogate Policy. In PM2.5
attainment (or unclassifiable) areas, the
new PSD requirements under 40 CFR
51.166 set forth the PM2.5 requirements
for states with SIP-approved programs
to include in their state PSD programs;
similar requirements were added to 40
CFR 52.21—the Federal PSD program—
for EPA (or, where applicable, delegated
state agencies) to use for implementing
the new PM2.5 requirements in states
lacking approved PSD programs in their
SIPs.
Although the 2008 PM2.5 NSR
Implementation Rule generally requires
states to begin implementing the new
PM2.5 requirements upon the July 15,
2008, effective date of the rule, EPA
provided two transition provisions
within the PSD program under specific
conditions. The first of these transition
provisions, a grandfather provision,
applied specifically to certain sources
that had applied for PSD permits
pursuant to the Federal PSD program
under 40 CFR 52.21. The second
transition provision allowed states to
continue using the 1997 PM10 Surrogate
Policy on an interim basis to implement
the PM2.5 requirements in any state PSD
program that is part of an approved SIP.
This latter exception was to apply to
permit reviews under state PSD
programs until the end of the 3-year SIP
development period (which ends in
May 2011) or until EPA approves the
revised state program, whichever comes
first.
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IV. Grandfather Provision for PM2.5 in
the Federal PSD Program
A. What is the grandfather provision for
PM2.5?
Under certain circumstances, EPA has
allowed proposed new major sources
and major modifications that have
submitted a complete PSD permit
application before the effective date of
an amendment to the PSD regulations,
but have not yet received a final and
effective PSD permit, to continue
relying on information already in the
application rather than immediately
having to amend applications to
demonstrate compliance with the new
PSD requirements. In such a way, these
proposed sources and modifications
were ‘‘grandfathered’’ or exempted from
the new PSD requirements that would
otherwise have applied to them. For
example, the Federal PSD regulations at
40 CFR 52.21(i)(1)(x) provide that the
owners or operators of proposed sources
or modifications that submitted a
complete permit application before July
31, 1987, (i.e., the effective date of the
revisions to the Federal PSD regulations
to implement the PM10 NAAQS) are not
required to meet the requirements for
PM10, but may instead satisfy the
requirements for total suspended
particulate matter (TSP) that were
previously in effect.
In addition, EPA has allowed some
grandfathering for permit applications
submitted before the effective date of an
amendment to the PSD regulations
establishing new maximum allowable
increases in pollutant concentrations
(also known as PSD increments). The
Federal PSD regulations at 40 CFR
52.21(i)(10) provide that proposed
sources or modifications that submitted
a complete permit application before the
effective date of the increments for PM10
in the applicable implementation plan
are not required to meet the increment
requirements for PM10, but may instead
satisfy the increment requirements for
TSP that were previously in effect. Also,
40 CFR 52.21(b)(i)(9) provides that new
sources or sources making modifications
that submitted complete permit
applications before the provisions
embodying the maximum allowable
increase for nitrogen oxides (the
nitrogen dioxide increments) took effect
are not required to demonstrate
compliance with the new increment
requirements to be eligible to receive the
permit.
Similarly, the 2008 PM2.5 NSR
Implementation Rule added a
grandfather provision allowing permit
applicants that had submitted a
complete application under the Federal
PSD program at 40 CFR 52.21 prior to
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the July 15, 2008, effective date, but had
not yet received their PSD permit by
that date, to continue being reviewed
using the 1997 PM10 Surrogate Policy.
The grandfather provision for PM2.5,
added as new paragraph (xi) to 40 CFR
52.21(i)(1), was not proposed for notice
and comment in the 2005 PM2.5
Implementation Rule proposal. Instead,
the 2005 PM2.5 Implementation Rule
proposal had provided that when we
issued the final rule, the new PM2.5
requirements would take effect
immediately in PSD permits issued in
states where the Federal PSD program
applies. See 70 FR 65986 at 66043.
As described more in the discussion
that follows in section IV.B of this
preamble, EPA has twice stayed the
grandfather provision for PM2.5, with the
first of the two stays beginning on June
1, 2009. Consequently, permits covered
by the grandfather provision that had
not already been issued by the effective
date of the first stay could not be issued
relying upon the 1997 PM10 Surrogate
Policy as the basis for approval during
the time periods that the stays remained
in effect.6 Prior to the stays, the
grandfather provisions remained in
effect from July 15, 2008, until June 1,
2009, during which time PSD permit
applications relying on the 1997 PM10
Surrogate Policy to satisfy the PSD
requirements for PM2.5 continued to be
acceptable for purposes of approving
and issuing the PSD permits.
B. Why did EPA propose to repeal the
grandfather provision for PM2.5?
On July 15, 2008, Earthjustice, acting
on behalf of the Natural Resources
Defense Council and the Sierra Club,
submitted a petition to the
Administrator seeking reconsideration
of four provisions of the 2008 PM2.5 NSR
Implementation Rule.7 One of the four
challenged provisions was the
grandfather provision for PM2.5 under
the Federal PSD program. In the
petition, the petitioners argued that
‘‘EPA unlawfully failed to present this
grandfather provision and
accompanying rationale to the public for
comment.’’ See July 15 Petition at 6.
Thus, petitioners argued, EPA had not
given interested parties any notice of
and the opportunity to comment on the
grandfather provision that EPA adopted
6 At the time the grandfather provision for PM
2.5
was put into effect, we estimate that fewer than
thirty proposed new or modified major stationary
sources were covered. Of these, at least two projects
subsequently received final and effective PSD
permits after the July 15, 2008, effective date of the
final rule and before the June 1, 2009,
administrative stay took effect.
7 Available in the docket for this rulemaking at
https://www.regulations.gov, document number
EPA–HQ–OAR–2003–0062–0279.1.
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in 40 CFR 52.21(i)(1)(xi) in the final
rule. Moreover, with regard to the
grandfather provision itself, the
petitioners questioned EPA’s authority
to waive statutory requirements by
establishing such a provision, and
argued that Congress specifically
addressed the issue of grandfathering in
section 168(b), where it allowed for the
grandfathering of only those sources on
which construction had commenced
before enactment of the 1977 Clean Air
Act Amendments. See July 15 Petition
at 7.
Finally, petitioners argued that the
technical difficulties associated with
ambient monitoring, estimating
emissions, and air quality modeling that
led to the adoption of the 1997 PM10
Surrogate Policy no longer existed.
Hence, the petitioners argued that all
sources must conduct the required
analyses for PM2.5 directly without
relying on the 1997 PM10 Surrogate
Policy, and, therefore, there was no
justification for continuing to allow any
sources to rely on the grandfather
provision. See July 15 Petition at 8. In
sum, petitioners asserted that the
grandfather provision in 40 CFR
52.21(i)(1)(xi) was illegal and arbitrary,
and requested that EPA stay the
provision.
On January 14, 2009, EPA responded
in a letter to the petitioners that the
Agency was denying all aspects of the
petition for reconsideration. However,
on February 10, 2009, the same
petitioners submitted a second petition
similar to thefirst to EPA.8
The second petition made the same
arguments that were presented in the
July 15, 2008, petition seeking
reconsideration and an administrative
stay and sought reconsideration of both
the 2008 PM2.5 NSR Implementation
Rule and the January 2009 denial of
petitioners’ first petition for
reconsideration. In response to the
second petition, the Administrator
reversed the Agency’s earlier decision
and agreed to reconsider each of the
four challenged provisions.
In a letter dated April 24, 2009, the
Administrator indicated that the Agency
would reconsider the grandfather
provision and propose to repeal the
grandfather provision ‘‘on the grounds
that it was adopted without prior public
notice and is no longer substantially
justified in light of the resolution of the
technical issues with respect to PM2.5
monitoring, emissions estimation, and
air quality modeling that led to the PM10
Surrogate Policy in 1997.’’ Finally, the
8 Available in the docket for this rulemaking at
https://www.regulations.gov, document number
EPA–HQ–OAR–2003–0062–0281.
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Administrator’s letter announced an
administrative stay of the grandfather
provision for 3 months under the
authority of section 307(d)(7)(B) of the
Act.
The 3-month administrative stay
became effective on June 1, 2009—the
date the notice announcing the stay was
published in the Federal Register—and
ended on September 1, 2009. See 74 FR
26098. In order to allow additional time
necessary to finalize this rulemaking,
EPA proposed and promulgated a
second stay that stayed the grandfather
provision until June 22, 2010. See 74 FR
48153, September 22, 2009. During the
second stay, on February 11, 2010, EPA
issued a notice of proposed rulemaking
that proposed repealing the grandfather
provision. See 75 FR 6827. The same
notice also proposed to end early the
use of the 1997 PM10 Surrogate Policy
in PSD programs implemented by states
under an approved SIP. EPA is taking
no final action on the latter proposed
action, as described further in section V
of this preamble.
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C. Summary of Comments and
Responses on the Proposed Repeal of
the Grandfather Provision
A total of 38 commenters, including 7
commenters speaking at the public
hearing held on February 26, 2010,
responded to the 2010 notice of
proposed rulemaking. Most of these
commenters specifically addressed the
proposed repeal of the grandfather
provision for PM2.5 in the Federal PSD
rule at 40 CFR 52.21(i)(1)(xi).
Seven commenters support the
proposal to repeal the grandfather
provision, while 20 expressly opposed
it. The commenters provided various
reasons for their positions. The
following discussion summarizes the
significant comments and our responses
categorized by specific topics. A more
detailed summary of the comments and
our responses is contained in the
Response to Comment document in the
docket for this rulemaking.
1. Comments on Legal Concerns
Comments on Legality of the
Grandfather Provision:
Some environmental group
commenters support EPA’s proposed
repeal, in part, because of their
interpretation that the grandfather
provision is illegal. The commenters
claim that EPA has no discretion to
waive or grandfather any permits under
the Federal PSD program. On the other
hand, 12 commenters disagree that there
is anything unlawful about the
grandfather provision for PM2.5. Those
commenters claim that EPA clearly has
the authority to establish a grandfather
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provision as part of a transition
procedure for implementing new
requirements. Some of these
commenters point out that EPA
indicated in the 2008 PM2.5 NSR
Implementation Rule that the
grandfather provision was consistent
with existing grandfather provisions
contained in 40 CFR 52.21(i)(1)(x).
Response:
We disagree with the comments
stating that EPA may not establish
grandfather provisions in appropriate
circumstances. Our decision to repeal
the grandfather provision here does not
reflect any conclusion by EPA that the
grandfather provision for PM2.5, or
grandfather provisions in general, are
unlawful. See also our response to the
following comments on statutory
authority.
Comments on Statutory Authority:
Several commenters argue against the
petitioners’ claim in the 2009 petition
for reconsideration that section 168(b) of
the Act restricts EPA’s ability to
grandfather sources by allowing for the
grandfathering of only those sources on
which ‘‘construction was commenced
* * * after June 1, 1975, and prior to
the enactment of the Clean Air Act
Amendments of 1977 * * *.’’ These
commenters argue that Congress’
inclusion of a one-time grandfather
provision upon enactment of the PSD
program is clearly different from
grandfathering when a new pollutant is
identified for regulation by a NAAQS,
which the Act does not address. These
commenters urge EPA to confirm that
the grandfather provision in section 168
(intended to ease transition upon
enactment of the PSD statute) does not
constrain the Agency with respect to
offering reasonable transition provisions
when pollutants become newly subject
to a NAAQS. The commenters argue
instead that the existence of the
grandfather provision in section 168
generally indicates that Congress
intended for smooth transitions to new
programs under the Act.
One of these commenters argues that
in the PSD program, EPA has included
grandfather provisions when it adopted
a number of new permitting
requirements, and that the Act gives
EPA substantial discretion to decide on
the specifics of PSD applicability.
(Citing Envt’l Defense v. Duke Energy
Corp., 127 S. Ct. 1423, 1433–34 (2007).)
Another of the commenters claims that
a repeal of the grandfather provision
would be unfair and contrary to the Act.
Finally, some commenters expressly
call upon EPA to clarify that it retains
the authority to issue transition policies,
such as the grandfather provision, when
new NAAQS are issued.
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Response:
We do not agree with the petitioners’
original claim that EPA lacks authority
to adopt and implement the grandfather
provision for PM2.5. Thus, we agree with
the commenters who also question the
petitioners’ claim. In particular, we do
not agree that the existence of certain
grandfathering in section 168(b) of the
Act is properly read to prohibit
grandfathering in all other
circumstances. As discussed previously
in section IV.A of this preamble, and as
pointed out in some of the comments,
we have relied on the use of grandfather
provisions in past NSR regulations
where we believed that it was
appropriate as part of the transition
process for implementing new
requirements. In the preamble to the
2008 PM2.5 NSR Implementation Rule,
we stated our position that the PM2.5
grandfather provision is consistent with
the existing provision under 40 CFR
52.21(i)(1)(x) whereby EPA
grandfathered new and modified major
stationary sources with permit
applications based on PM (measured as
TSP) from the then-new PM10
requirements established in 1987.
However, while we continue to believe
that we have the discretion to use
grandfather provisions in the PSD
program where appropriate, we have
decided to repeal the grandfather
provision for PM2.5 at 40 CFR
52.21(i)(1)(xi) on policy grounds, as
discussed later in this preamble.
Comments on the Section 165(c)
Requirement To Issue a PSD Permit
within 1 Year:
One commenter points to section
165(c) of the Act as creating a 1-year
deadline for issuing a PSD permit after
a complete application has been
submitted, and argues that since most,
if not all, of the permit applications that
would be affected by the repeal of the
grandfather provision were likely
submitted more than 1 year before the
initial (administrative) stay of the
grandfather provision took effect, those
applications are entitled to final action
consistent with the grandfather
provision and the use of PM10 as a
surrogate for PM2.5. The commenter
further argues that, in addition to
allowing EPA or states with delegated
PSD authority to continue ongoing
violations of the section 165(c) deadline,
repealing the grandfather provision for
PM2.5 would deepen and perpetuate the
‘‘unlawful’’ effects of the stay.
Response:
We do not dispute that some of the
permit applications relying on the
grandfather provision were not granted
or denied within the 1-year period
provided in section 165(c) of the Act,
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but disagree that this is a valid
justification for allowing the use of the
grandfather provision, for all of the
reasons discussed in this preamble. In
making this comment, the commenter
has not shown that the failure to act on
those applications within 1 year can be
attributed to the stays of the grandfather
provision (which, as the commenter
recognizes, came into effect almost 1
year after the grandfather provision for
PM2.5 was promulgated). Indeed, the fact
that a permit was not issued within a
year during the time that the grandfather
provision was in effect suggests that
there were other factors that prevented
the source from receiving a permit
within the 1-year period provided by
CAA section 165(c). Moreover, even if
the grandfather provision had not been
stayed with respect to those pending
applications (or if the 1997 PM10
Surrogate Policy were to become
available to the applicant through some
other mechanism in the future), it is not
clear that the applications provided the
information or analyses necessary under
the case law to demonstrate that PM10
is a reasonable surrogate such that the
1997 PM10 Surrogate Policy could be
used. See, e.g., discussion of case law in
75 FR 6827, 6831–32 (February 11,
2010). Finally, if the applicant believes
that it can demonstrate that surrogacy is
consistent with the case law, then it
may do so under the case law even in
the absence of EPA’s 1997 PM10
Surrogate Policy.
Comments on the Legality of
Repealing the Grandfather Provision for
PM2.5:
Some commenters opposing the
proposed repeal of the grandfather
provision for PM2.5 argue that the repeal,
in addition to the second petition for
reconsideration, is illegal. With regard
to the repeal action, some commenters
question EPA’s alleged position that it
must repeal the grandfather provision
because there was not adequate notice
to the public of EPA’s intent to continue
the use of the 1997 PM10 Surrogate
Policy. The commenters disagree with
this position, claiming that a failure to
provide for notice and comment on a
provision of a rule cannot be a reason
to repeal that provision.
One commenter disputes that there
was inadequate notice because technical
difficulties of measuring, modeling, and
monitoring PM2.5 have been well known
since 1997 and were fully documented
during the rulemaking. Thus, the
commenter asserts that EPA lacked the
technical basis to require sources that
had complete applications pending at
that time of the promulgation of the
2008 PM2.5 NSR Implementation Rule to
measure or predict PM2.5 concentration.
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In addition, this commenter asserts that
EPA failed to meet the administrative
requirements for terminating the 1997
PM10 Surrogate Policy. Specifically, the
commenter states that EPA would have
had to provide notice of the withdrawal
of the 1997 PM10 Surrogate Policy to
reverse its use by sources grandfathered
by the final 2008 PM2.5 NSR
Implementation Rule.9 Based on these
assertions, the commenter contends that
EPA may not repeal the grandfather
provision retroactively.
Two commenters believe that the
grandfather provision, while not
explicitly proposed, was a logical
outgrowth of the proposal. One of the
commenters expresses the belief that
EPA raised for comment, in the 2005
PM2.5 Implementation Rule proposal,
issues concerning appropriate means for
and timing of the transition to
implementation of PM2.5 requirements
in the PSD program. The other
commenter alleges that the 2005 PM2.5
Implementation Rule proposal expressly
announced continued use of the 1997
PM10 Surrogate Policy as Option 1 at 70
FR 66044 and solicited comment on this
approach.
The latter commenter also argues that
the 2010 proposal to repeal the
grandfather provision for PM2.5
represents a dangerous procedural
precedent. While acknowledging that
some actions adopted in a final rule
could clearly be outside the scope of the
proposed rule, the commenter asserts
that as an overarching rule, the
determination of whether regulatory
actions adopted by a previous
Administration’s final rule were a
logical outgrowth of the proposed rule
should be left for the courts to decide.
The commenter believes that leaving
such decisions to the courts will ensure
objective and consistent determinations
of administrative law, rather than
politically-influenced determinations
that likely will shift from
Administration to Administration. The
commenter contends that the
grandfather provision is not an instance
that warrants EPA’s departure from that
principle.
One commenter claims that the issue
of the lawfulness of the grandfather
provision was previously addressed and
decided by EPA in the January 14, 2009,
denial of the first petition for
reconsideration of the final 2008 PM2.5
NSR Implementation Rule. The
commenter contends that EPA’s reliance
9 In support of this position, the commenter cites
Appalachian Power v. EPA, 208 F.3d 1015, 1028
(D.C. Cir. 2001); Alaska Professional Hunters
Association v. FAA, 177 F.3d 1030, 1033–34 (D.C.
Cir. 1999); and Paralyzed Veterans of America v.
D.C. Arena L.P., 117 F.3d 579, 586 (D.C. Cir. 1997).
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on the second petition for
reconsideration, filed on February 10,
2009, is contrary to section 307(d)(7)(B)
of the Act because the second petition
did not contain any new information
that would justify reconsideration and,
thus, the second petition was untimely
and unfounded.
Response:
We do not agree with the commenters’
claim that we are repealing the
grandfather provision because of the
lack of adequate notice to the public.
The lack of prior public notice was a
basis only for granting reconsideration
and going through a subsequent
rulemaking. EPA’s decision to repeal the
grandfather provision is not based on
the fact that the provision was not
explicitly proposed in the 2005 PM2.5
Implementation Rule proposal. EPA in
this rule is not taking any position on
whether a lack of public notice could be
a basis for repealing a rule, or on the
other issues that these comments raise
concerning the adequacy of public
notice, logical outgrowth, the timeliness
of the second petition for
reconsideration, and other procedural
matters.
We believe that the Act provides EPA
with sufficient authority to issue
transition policy, including grandfather
provisions, as needed to provide for the
reasonable implementation of new NSR
requirements. This is evidenced by the
fact that we have established
grandfather provisions in the past, as
described in section IV.A of this
preamble. However, it should not be
taken to mean that we have or intend to
automatically use grandfathering as a
transition mechanism for all changes in
NSR requirements. In this case, we
continue to believe that the technical
tools needed to carry out a PM2.5
analysis are currently available to the
degree necessary to justify requiring
sources to comply with the PM2.5
requirements via PM2.5 analyses for
BACT and air quality impacts. Indeed,
this is what all other sources that are not
subject to the grandfather provision but
are located in areas subject to the
Federal PSD program are required to do.
Alternatively, sources may use an
appropriate surrogacy demonstration in
accordance with past court decisions.
For this reason and the other
substantive reasons discussed in this
preamble, we have decided to repeal the
grandfather provision for PM2.5.
Finally, we wish to clarify a point
made by the commenter who alleged
that the 2005 PM2.5 Implementation
Rule proposal expressly announced and
sought comment on the continued use
of the 1997 PM10 Surrogate Policy as
Option 1. That proposal actually
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proposed to allow the continued use of
the 1997 PM10 Surrogate Policy only for
states that have SIP-approved PSD
programs and need additional time to
revise their rules to address the PM2.5
requirements. For all other
circumstances involving the NSR rules,
we clearly stated that PSD applicants
would be subject to the PM2.5
requirements as of the effective date of
the final rule. See 70 FR 66043–44.
2. Comments on the Burden on Sources
Resulting From Repeal of the
Grandfather Provision
In the 2010 proposal to repeal the
grandfather provisions for PM2.5, EPA
solicited comments on the burdens that
may be incurred by sources affected by
a repeal of the grandfather provision.
See 75 FR 6833. Several commenters
express concern that repeal of the
grandfather provision would unfairly
penalize permit applicants who were in
the process of obtaining construction
permits.
Comment:
One commenter states that repeal
would effectively impose retroactive
requirements on sources that relied on
past EPA statements of the law and the
effect of the Agency’s regulations, which
goes against the concepts of
fundamental fairness and equity.
Response:
We disagree with the premise of this
comment: that the repeal of the
grandfather provision imposes new
requirements. The 1997 PM10 Surrogate
Policy did not eliminate any PSD
requirements; it simply provided an
alternative means of demonstrating
compliance with the applicable
requirements that were already in the
PSD regulations at 40 CFR 52.21 when
the PM2.5 NAAQS became effective in
1997. Thus, the repeal of the grandfather
provision does not impose new
requirements on any source. The
commenter’s concern about the fairness
of our decision is addressed in the next
response.
Comment:
Some commenters indicate that repeal
would result in ‘‘permit gridlock.’’ These
commenters state that each regulatory
change adds another year onto the
permitting process, during which more
regulations could change and add
further delay. The commenters contend
that because of the length of the process,
the major applicable rules need to stay
constant (in all but extraordinary
circumstances) in order for the process
to proceed in a logical and orderly
fashion.
Another commenter claims that repeal
of the grandfather provision would
arbitrarily and unreasonably penalize
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applicants for the delay of the reviewing
authority in discharging its permitting
responsibilities. The commenter
provides an example where two
applicants (Applicants A and B) submit
complete applications on the same date
more than a year before the effective
date of the stay of the grandfather
provision, but Applicant A’s permit is
approved and issued before the effective
date of the stay and Applicant B’s
permit is not yet ready to be issued on
the effective date of the stay. The
commenter concludes that, through no
fault of Applicant B, EPA’s violation of
its nondiscretionary statutory duty to
act within 1 year would impose on the
applicant the significant costs and delay
involved in undertaking a new analysis
of PM and, potentially, revising the
permit application.
One commenter opines that an
important principle underlies all
grandfather provisions, including this
PM2.5 grandfather provision. This
principle is that a source that relies in
good faith on EPA’s existing standards
and procedures to design a construction
project and prepare a PSD permit
application based upon that design
should have the right to rely upon those
existing standards and procedures and
should not later be penalized
retroactively when the standards and/or
procedures change and, more
importantly, go into effect after the
application was submitted.
The same commenter goes on to point
out that the issuance of a PSD permit
under the grandfather provision would
not establish any future waiver of
compliance or long-term exemption
under law or in practice because the Act
requires all sources, including those that
have undergone PSD review, to comply
with limitations the state determines in
its SIP are necessary to meet NAAQS
(including any future revised NAAQS)
as well as to comply with any New
Source Performance Standards.
According to the commenter, this
ensures that, regardless of whether a
source avoided direct evaluation of its
PM2.5 emissions during NSR because of
the grandfather provision, its PM2.5
emissions will still be evaluated for
compliance with the PM2.5 NAAQS.
Response:
In projecting the burdens of extended
permitting time and effort, the
commenters assume that if we did not
repeal the grandfather provision,
sources could rely on the 1997 PM10
Surrogate Policy without further
analysis. However, as discussed in the
2010 proposal preamble (see 75 FR
6831–32) and later in section V.C.1.b of
this preamble, at present sources are
only able to use the policy after
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completing a surrogacy demonstration
consistent with the case law (i.e., PM10
must be shown to be a reasonable
surrogate for PM2.5 under the
circumstances of the specific permit)
and within the limits of the policy itself
(i.e., there must be continuing technical
reasons why a PM2.5 analysis is not
technically feasible). These key
prerequisites cannot be assumed to be
met automatically, and the commenters
have not shown these prerequisites to be
met with respect to any of the
applications that would be covered by
the grandfather provision. Thus, even if
the grandfather provision were to
remain in force, additional analysis
would be required of sources seeking to
continue using the 1997 PM10 Surrogate
Policy under that provision.
The EPA has considered the
comments concerning how a repeal of
the grandfather provision might impact
the permitting process and allegedly
create unfairness and inequity in some
of the hypothetical circumstances
described in the comments. We
recognize that the commenters’
concerns pertain to the fairness of our
proposal to change the procedures for
demonstrating compliance with the
PM2.5 requirements in mid-permit
process for individual permits.
However, we believe that we have an
obligation to weigh those concerns and
associated burdens against our
interpretation of the Act, which requires
that PSD sources must demonstrate that
their emissions will not cause or
contribute to a violation of the PM2.5
NAAQS, and such demonstration
should provide adequate assurance that
such compliance will occur. We believe
that the 1997 PM10 Surrogate Policy,
which has been in effect for about 13
years, no longer provides an acceptable
means of making the required
demonstration in light of the availability
of the technical tools needed to
complete a PM2.5 analysis. Thus, as part
of our obligation to evaluate the need for
transition policy both initially and on
an ongoing basis, we have concluded
that such burdens are neither unfair nor
inequitable in comparison to the
benefits associated with having a better
understanding of the impacts the
source’s emissions will have on the
PM2.5 NAAQS. This conclusion is based
on our belief that the approach set forth
in the 1997 EPA policy memo, while
necessary in the absence of the technical
tools needed to implement the PSD
program for PM2.5 directly, is
sufficiently deficient in its ability to
satisfy the PM2.5 requirements (in that it
lacks a surrogacy demonstration),
particularly with regard to possible
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adverse impacts on the PM2.5 NAAQS,
that it should no longer be available as
a means of meeting those requirements
now that the necessary technical tools
for a PM2.5 analysis are available. Case
law allows the use of surrogates when
properly applied. Hence, we point out
that the use of a valid surrogate
approach in general is not prohibited by
our action in this final rule.
Finally, we note that we did not stay
the grandfather provision until almost 1
year following its effective date. Some
permits were issued during the time that
the grandfather provision was in effect.
Grandfathered sources for which a PSD
permit was not issued during that
period likely had problems related to
factors other than the PM2.5 analyses
that prevented the source from receiving
a permit.
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3. Comments on the Number of Sources
Affected by Repeal
Comment:
We did not receive any comments that
either validate or dispute the number of
sources that we estimated would be
affected by the stay of the grandfather
provision for PM2.5.10 One commenter
observes that EPA has recognized that
continued use of the grandfather
provision would affect very few, if any,
still-pending permits, and finds it hard
to understand why EPA feels it
necessary not only to discontinue the
grandfather provision altogether, but
also to do so immediately by issuing the
administrative stay. This commenter
believes that the facts presented by EPA
undercut the petitioners’ claim that
grandfathering certain permit
applications presents an irreparable
harm.
Response:
In the 2010 proposal to repeal the
grandfather provision, we reported that
we were aware of 27 sources that had
submitted PSD permit applications
under the Federal PSD program prior to
July 15, 2008— the effective date of the
2008 PM2.5 NSR Implementation Rule—
but did not receive their permits by that
date. Thus, these applications fell
within the scope of the grandfather
provision at the time it was
promulgated. For at least six of these
applications, the permit was either
10 A state agency commenter claims that EPA’s
repeal of the grandfather provision for PM2.5 could
affect up to 16 of the agency’s pending PSD
projects. However, this agency’s PSD program is
part of an EPA-approved SIP and, as such, does not
appear to be affected by the grandfather provision.
Instead, we believe that the affected PSD projects
would be affected by the ending of the 1997 PM10
Surrogate Policy. Thus, we address this comment in
the section V, where our final action on ending the
1997 PM10 Surrogate Policy in SIP-approved PSD
programs is addressed.
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issued or denied, or the project was
cancelled, prior to June 1, 2009, when
the administrative stay became effective.
For most of the remaining 21
applications, it is our understanding
that the sources have already directly
addressed, or are planning to directly
address, the applicable PM2.5
requirements in order to obtain a
permit. At least two of the sources are
reportedly planning to take enforceable
emissions limitations on their PM2.5
emissions in order to avoid the PSD
requirements for PM2.5 altogether.
Although only a few remaining
grandfathered sources would be affected
by a repeal of the grandfather provision,
we believe that any air quality
assessment contained in a PSD permit
should reflect as accurately as possible
the actual impacts that could be
experienced in the area of concern. We
do not believe that an analysis of PM10
emissions impacts on the PM10 NAAQS
sufficiently represents the potential
impacts that a source may have on the
PM2.5 NAAQS. We did not base our
decision to repeal the grandfather
provision on the number of sources that
could ultimately have to submit revised
analyses to satisfy the PSD requirements
for PM2.5.
4. Comments on Retroactive
Implementation
Comment:
Several commenters who oppose the
proposed repeal of the grandfather
provision support a position, based on
a statement by EPA in the 2010
proposal, that a repeal of the grandfather
provision would not impact any PSD
permits that relied on the 1997 PM10
Surrogate Policy that became final and
effective before the stay of the provision.
See 75 FR 6833. However, one
commenter who supports repealing the
grandfather provision takes exception to
those opposing commenters’ position
and requests a clarification as follows:
To the extent EPA is saying simply that the
repeal does not change the defensibility of a
source’s reliance on the illegal policy, we
agree. But EPA should clarify that it is not
claiming that its action somehow protects
past illegal permitting decisions. The
Surrogate Policy is and always has been
illegal. Reliance on this illegal policy is
subject to challenge and cannot be protected
by EPA preamble statements that lack any
authority or force of law.
Response:
Neither EPA’s repeal of the
grandfather provision nor its ending of
the 1997 PM10 Surrogate Policy in SIPapproved states changes the
defensibility of a source’s previous
reliance on the 1997 PM10 Surrogate
Policy. Put another way, repeal of the
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grandfather provision and the ending of
the 1997 PM10 Surrogate Policy does not
create a new basis for arguing that the
permit was not properly issued.
However, a challenge to a permit that is
not based on the repeal itself (such as
a challenge claiming that the 1997 PM10
Surrogate Policy did not provide a valid
means of meeting the CAA requirements
or that the policy was not applied
properly to the permit being challenged)
is not impacted by repealing the
grandfather provision for PM2.5.
5. Comments on the Technical Tools
Needed for a PM2.5 Analysis
Some of the commenters responding
to the 2010 proposal to repeal the
grandfather provision for PM2.5 agree
with EPA’s conclusion that the
technical issues associated with the
implementation of a PSD program for
PM2.5 have been largely resolved.
However, most of the commenters
believe that the necessary technical
tools for PM2.5, i.e., ambient monitoring
data, emissions data (including
emissions inventories, emissions
factors, and stack testing methods), and
air quality modeling techniques, are not
yet sufficiently available to carry out an
adequate analysis for PM2.5. One
commenter claims that technical
problems continue to exist and points
out that even EPA has acknowledged
that some technical issues remain to be
addressed. The commenter states that
this shows EPA has not satisfied its
burden to establish that the PM2.5
program can be implemented by states.
Response:
We do not agree with the commenter’s
claim that because some technical
issues remain to be addressed, we
should not require applicants to begin
carrying out a PM2.5 analysis to satisfy
the PSD requirements. We believe that
there is a sufficient technical basis to
allow sources to begin focusing on PM2.5
emissions and direct demonstrations of
compliance with the PM2.5 standards
without the use of surrogates. In the
March 23, 2010, EPA modeling
guidance memorandum titled,
‘‘Modeling Procedures for
Demonstrating Compliance with the
PM2.5 NAAQS,’’ we provide procedures
that help an applicant complete both a
preliminary significant impact analysis
and a cumulative impact analysis to
determine the impact of a PSD source or
modification on the PM2.5 NAAQS.11
In addition, we have recently
addressed some of the important
components of the PSD program for
11 This guidance memorandum for PM
2.5
modeling can be found on EPA’s Web site at
https://www.epa.gov/ttn/scram.
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small fraction of particles greater than
2.5 μm are included in the PM2.5 mass
concentration measurement. As an
example, less than 2 percent of 3.2 μm
particles in the ambient air are included
in the mass concentration measurement,
and virtually all particles larger than
this size are totally excluded from the
PM2.5 mass concentration measurement.
Therefore, concerns regarding potential
PM2.5 mass measurement bias associated
with large ambient particles are
unfounded. As a result, the PM2.5 FRM
provides accurate PM2.5 mass
concentration measurements for
purposes of determining compliance
with the PM2.5 NAAQS, and for
evaluating the effectiveness of PM2.5
control initiatives.
Comment:
a. Comments on Ambient Monitoring
Some commenters believe that some
Data
states may not have adequate ambient
Comment:
monitoring data to determine ambient
One state agency commenter states
background levels. A commenter claims
that ambient air monitoring data may
that many states do not yet understand
not represent ‘‘true’’ PM2.5
or have sufficient PM2.5 ambient data to
concentrations because the Federal
support the regional modeling
Reference Monitors include particle
initiatives, which would make assessing
sizes above PM2.5 in the PM2.5 particle
and enforcing the PM2.5 NAAQS
count. The commenter believes that it is difficult and problematic for both the
difficult to evaluate PSD and minor NSR regulators and the regulated community.
permits without representative ambient
Response:
States have been operating a large and
monitoring data to verify the accuracy
robust network of PM2.5 samplers since
or appropriateness of emissions factors
1999. As part of each state’s required
and dispersion modeling predictions.
Response:
monitoring network, each stack is
As part of its periodic review of the
required to have a least one PM2.5 site
NAAQS, EPA recently evaluated the
to monitor for regional background and
latest available science for PM in its
at least one PM2.5 site to monitor for
‘‘Integrated Science Assessment (ISA)
regional transport. See section 4.7.3,
for Particulate Matter’’ (EPA, 2009). This Appendix D to 40 CFR part 58. While
document included a discussion of
there is flexibility in the location and
Federal Reference Methods (FRMs) and
methods used for these sites, given the
other PM test methods. Also, FRMs and spatial uniformity of PM2.5 compared to
Federal Equivalent Methods for PM
PM10 and the large number of PM2.5
were discussed in detail in the 2004 PM samplers operating, EPA believes there
Air Quality Criteria Document (EPA,
are sufficient PM2.5 data to support data
2004). These discussions document the
needs such as modeling.
fact that the size-selective nature of the
Comment:
FRM for PM2.5 was developed based on
Another commenter claims that there
is no guidance available on how to
epidemiological studies which used
determine representative (and
ambient fine particle sampler
measurements as indicators of exposure. reasonable) PM2.5 background
The position and shape of the PM2.5
concentrations for air quality modeling
FRM’s fractionation curve was specified analyses. The commenter contends that
applying the current EPA-approved
as a means of separating particles
methodologies for determining
contained in the fine-thoracic regime of
background concentrations to PM2.5
ambient aerosols (e.g., those generated
by combustion, coagulation,
would result in background
condensation) from those particles
concentrations of PM2.5 in excess of 80
produced by other mechanisms (e.g.,
percent (and many cases in excess of 95
mechanically generated). The PM2.5
percent) of the NAAQS for PM2.5 for vast
FRM was not designed nor intended to
areas of the United States, which would
collect all particles less than 2.5
leave a PM2.5 emission source only an
micrometers (μm) aerodynamic diameter allowable air quality impact (as
while excluding all particles greater
determined from modeling) of 1–4 μg/
than 2.5 μm aerodynamic diameter.
m3. According to the commenter, even
Even so, the slope of the PM2.5 FRM’s
a small (less than 25 MMBtu/hr) natural
gas-fired boiler or a baghouse with an
fractionation is quite sharp and only a
wwoods2 on DSK1DXX6B1PROD with RULES_PART 1
PM2.5 that were described by various
commenters. We published a final rule
to revise the PM test methods to
measure in-stack concentrations of
PM2.5 emissions and condensables on
December 21, 2010, at 75 FR 80118. As
discussed further in section IV.C.6 of
this preamble, we issued the final rule
containing the PM2.5 increments, SILs,
and SMC on October 20, 2010, at 75 FR
64864. All of these documents, along
with the availability of ambient
monitoring data and the other necessary
tools that we describe in our responses
to comments that follow, provide a
sound and sufficient technical basis for
completing necessary analyses of
impacts of proposed sources on PM2.5
ambient levels.
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28655
allowable emission limit of as little 0.2
lb/hr will typically have an impact
greater than 1–4 μg/m3. The commenter
believes that without additional
guidance, neither of these types of small
sources could be permitted.
Response:
Generally, the ambient monitoring
data used as part of the cumulative
analysis should represent
concentrations from emissions from
existing sources that are not also being
modeled. However, based on recent
guidance contained in the March 23,
2010, EPA modeling guidance
memorandum titled, ‘‘Modeling
Procedures for Demonstrating
Compliance with the PM2.5 NAAQS,’’ 12
we recommend a different approach for
PM2.5, which reflects the fact that
secondary (precursor) impacts on
ambient PM2.5 concentrations from
individual source emissions cannot
adequately be estimated by currentlyaccepted modeling techniques. That is,
we recommend that the monitoring data
for PM2.5 account for the contribution of
secondary PM2.5 formation
representative of the area being modeled
for the proposed PSD source. See March
23, 2010, Guidance, at pages 7–8. To the
extent that accounting for precursor
impacts involves sources from which
PM2.5 emissions are also being modeled,
the March 23, 2010, guidance states (at
page 7) that the double-counting
problem generally will be of less
importance for PM2.5 than the
representativeness of the monitor for
secondary contributions. We also intend
to address separately more detailed
guidance on the determination of
representative background data for
PM2.5.
b. Comments on Emissions Factors and
Emissions Inventories
Comment:
Several state agency and industry
commenters cite continued problems
with inadequate emissions factors and
emissions inventories for estimating the
amount of PM2.5 being emitted from a
new project or from existing sources
that must be modeled to demonstrate
compliance with the PM2.5 NAAQS. For
example, one commenter states that
there is extremely limited information
concerning emissions factors for PM2.5
from industrial sources, without which
it is not possible to accurately model the
impacts of PM2.5. Another commenter
states that emissions inventory data for
PM2.5 are in development and grossly
incomplete. Another commenter
disputes EPA’s claim that emissions
factors and emissions inventory data are
12 https://www.epa.gov/ttn/scram.
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readily available, stating that such
information is not yet readily available
in a quality-assured format on a sourceby-source and point-by-point basis as
needed for regulatory permitting
analyses. Another commenter adds that
while progress has occurred since 2008,
the inventories are far from complete
and EPA has yet to finalize a PM2.5 test
method.
A state agency commenter claims that
representative emission factors are not
available for the majority of industries.
The commenter adds that EPA clearly
stated in the preamble to the final 2007
PM2.5 Implementation Rule (citing 72 FR
20654–55, April 25, 2007) that the
quality of available direct filterable and
condensable PM2.5 national industry
average emissions factors, such as those
found in EPA’s ‘‘Compilation of Air
Pollutant Emission Factors’’ (AP–42), is
often insufficient to establish effective
source-specific emissions limits, and
expected states to rely on directly
measured emissions data.
The same commenter recognizes the
caveats related to using the factors in
AP–42, but states that often these factors
are the ‘‘best or only method available
for estimating emissions, in spite of
their limitations’’ (quoting from AP–42,
Volume I, Fifth Edition, January 1995,
Introduction to AP–42). The commenter
concludes that while EPA advised
stakeholders of its concern related to
PM2.5 implementation in 1997, EPA has
not updated many of the emissions
factors. In addition, the commenter
believes that factors for condensable
emissions are suspect due to the use of
a test method EPA is currently seeking
to revise, and directly measured data to
develop realistic emissions factors are
not available for many industries at this
time.
Response:
We believe that progress has been
made in the development of emissions
factors for PM2.5 since the time the
comments were submitted. When EPA
established a transition period for NSR
purposes in 2008 waiving the
requirement that states address
condensable PM in establishing
enforceable emissions limits for either
PM10 or PM2.5 in NSR permits, it was to
provide time for sources and state/local
reviewing authorities to improve the
emissions factors for the filterable and
condensable PM that they need for the
development of emissions inventories,
source-specific emissions, and control
levels achievable with emissions
controls. See 73 FR 28334–35 (providing
a waiver until January 1, 2011, unless
the SIP or applicable permit condition
otherwise required their inclusion).
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The Agency knows of several states
and other organizations that have
improved their ability to accurately
characterize these emissions. For
example, the Mid-Atlantic Regional Air
Management Association (MARAMA)
conducted a study to identify emissions
tests that employed EPA’s
recommended procedures under Test
Method 202, promulgated in 1990. The
emissions factors developed by
MARAMA are expected to be superior
to the latest published AP–42 emissions
factors even though both efforts
attempted to eliminate tests that did not
use the recommended options to
minimize artifact formation. Also, the
State of Pennsylvania and the San
Joaquin Valley United Air Pollution
Control District in California have
performed or required the performance
of tests using Other Test Method (OTM)
27 and/or OTM 28 to better characterize
the emissions of PM2.5 from sources and
source categories from which they
believed improved emissions
information was needed.13
Although the final revised test
methods for PM2.5 were only recently
promulgated, on December 21, 2010,
EPA has had a long history of
supporting the use of improved
procedures to perform particle sizing at
2.5 micrometers using modifications of
Method 201A, to employ procedures
included in the 1990 version of Method
202 for condensable PM, and to employ
the additional changes included in OTM
28 for condensable PM (to minimize
artifact formation).
As part of the Information Collection
Requests that EPA has issued to sources
in support of the development of
standards for select source categories,
we have required testing using OTM 27
(for PM2.5 only) and OTM 28. These
emissions data are being used by EPA in
the rule development process. These
data are also now available for sources
and states to use in the development of
improved emissions factors, emissions
inventories, source emissions estimates,
control measures evaluations, and
development of applicable
requirements.
With regard to comments regarding
the adequacy of existing emissions
inventories, we respond that, while the
National Emissions Inventory (NEI) and
state SIP inventories are evolving, their
quality is sufficient for permit modeling
13 These OTM methods represent improved
methods for measuring PM2.5 emissions, including
condensable PM2.5. These and other OTM methods
have not yet been subject to the Federal rulemaking
process, but have been reviewed by EPA’s
Emissions Measurement Center staff and placed on
the EPA Web site at https://www.epa.gov/ttn/emc/
prelim.html.
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for including the emissions sources
other than the source(s) being permitted.
The NEI generally uses the best
available information and much of that
information is supplied by the states.
States can take advantage of new data
stemming from OTM 27 and OTM 28, as
mentioned previously, to further
improve their inventory estimates in the
2009 inventory years and beyond. A
preliminary version of the 2008 NEI has
been made available to state and local
agencies, tribes and EPA Regional
Offices, and an updated version is
scheduled to be posted on EPA’s Web
site for public availability in April of
2011, to support future modeling efforts.
The NEI and state inventories will
continue to improve as emission factors
become available based on the new
PM2.5 test method.
The EPA also has been supplementing
the inventories provided by the states
with estimates of condensable PM
emissions for many years. These
estimates have included particle sizing
at 2.5 micrometers of the filterable PM
and the addition of CPM. We recognize
that there are some source categories
where the condensable PM emissions
may be biased high due to artifact issues
and that some source categories where
the condensable PM emissions are
biased low due to permitted
adjustments to test data and absence of
condensable PM testing. We do not
think that these inventory uncertainties
justify not using the available data to
develop inventories; we believe that
ignoring this information introduces
greater error than using the data. The
EPA believes that sources and states
should use these data as criteria for
identifying areas needing emissions
testing to correct biases. We will
respond to comments concerning the
test methods for PM2.5 in the
immediately following subsection.
c. Comments on the In-Stack Emissions
Test Method for PM2.5
Comment:
Closely tied to the comments citing a
lack of adequate emissions factors for
PM2.5 are comments claiming the lack of
an adequate test method for measuring
direct PM2.5 emissions—especially
condensable PM emissions. Some
commenters argue that it would be
inappropriate for EPA to repeal the
grandfather provision and require
applicants to complete a PM2.5 analysis
without the use of a surrogate until
adequate PM2.5 emissions test methods
are adopted by EPA.
One commenter claims that without
final rules on test methods, the state
agency is without specific authority to
require applicants to comply with this
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portion of the PM2.5 requirements. An
industry commenter expresses concern
with being required to perform an
emissions test to demonstrate
compliance with a PSD permit PM2.5
emissions limit when there are no
federally approved methods, and with
significant remaining technical issues
associated with the test methods for
measuring PM2.5.
Another industry commenter states
that although EPA has proposed
revisions to existing Method 201A to
allow measurement of filterable PM2.5,
the revised method is not final, and it
is not applicable to units with entrained
moisture droplets in the stack (e.g.,
units with wet stacks due to wet flue gas
desulfurization (FGD)). Because many
sources (including many large electric
generating units) use wet FGD to control
sulfur dioxide emissions and therefore
will be unable to use proposed revised
Method 201A, the commenter sees no
justification for the conclusion that the
technical issues associated with
measuring PM2.5 have been resolved.
Some commenters indicate that
problems associated with unacceptable
artifact levels in existing test methods
can overstate the results when sampling
for PM2.5 emissions.
Response:
We acknowledge the problems that
some states and sources have
experienced with sampling PM2.5
emissions. Until recently, EPA Federal
Register test methods have been
primarily used for determining
compliance with EPA regulations
published in parts 60, 61, and 63.14 We
have not seen a need to publish source
test methods in the Federal Register
that are primarily for other regulatory
purposes, such as compliance with
NAAQS-related permit limits. As a
result, many air pollutants or precursor
compounds do not have a promulgated
Federal test method. Also, the Federal
Register test methods do not address all
possible stack or pollutant release
conditions. We provide test methods on
our Emissions Measurement Center Web
site 15 that can be used to quantify an
extended range of pollutants and an
extended range of release conditions.
While not complete, these measurement
methods provide a resource for states to
14 Federal Register test methods are methods that
have been proposed in the Federal Register for
public review and comment. When those methods
are promulgated they become the official Code of
Federal Regulations Methods, which may be used
individually or in combination with other methods
by Federal, State or local agencies or sources to
quantify emissions cited by the regulations for
which the methods were developed and within the
limitations specified in the method itself without
further EPA approval.
15 https://www.epa.gov/ttnemc01/.
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supplement the available Federal
Register test methods.
We note, however, that on March 25,
2009, EPA proposed amendments to
Methods 201A and 202—in-stack test
methods for PM. See 74 FR 12970. For
Method 201A, we proposed to add a
particle-sizing device to allow for
sampling of PM2.5. For at least 5 years
prior to the test method proposal, EPA
provided guidance addressing the
majority of the artifact formation
associated with the 1991 published
version of that method.16 As mentioned
previously, the final test method rule
was promulgated on December 21, 2010,
and became effective on January 1,
2011. The amendments to Method 202
revise the sample collection and
recovery procedures of the method to
reduce the formation of reaction artifact
levels that could lead to inaccurate and
overstated measurements of
condensable PM. The amendments to
Method 202 also result in increased
precision of the method and improve
the consistency of measurements
obtained between source tests
performed under different regulatory
authorities.
As noted by the commenters, at this
time there is no recognized method for
quantifying PM2.5 emissions from
sources that have entrained water
droplets. We have an active effort to
develop a test method that can be used
under such conditions, but at this time
it is unclear whether a suitable test
method can be developed. As provided
in the proposed revision to Method
201A, we believe that until the test
method development is complete, the
use of EPA Method 5 provides a
reasonable substitute for a stack
condition-specific test method that
performs particulate sizing at 2.5
micrometers.
Even before the final test method rule
revising Methods 201A and 202 was
finalized, for a number of years, we had
been posting guidance on our Web site
for measuring emissions of PM2.5,
including the condensable fraction.17
The equipment, supplies, and
procedures provided by this guidance
have been improved over time by
stakeholders who have submitted
constructive comments. We believe this
posted guidance has provided a
reasonable means to quantify emissions
that are suitable for use in developing
emissions inventories; for developing
16 EPA guidance on predecessors for Method
201A can be found at https://www.epa.gov/ttn/emc/
prelim.html and https://www.epa.gov/ttn/emc/
ctm.html.
17 In addition to the Web sites identified in the
earlier footnote, see also https://www.epa.gov/ttn/
emc/methods/method202.html.
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information that is useful in developing
appropriate achievable emissions levels
for sources; and for assessing the
performance of a source’s PM controls.
We recognize that it is desirable to
provide detailed documentation of the
conduct of source test methods such
that there is consistency between
establishing the applicable requirements
and the method used to demonstrate
compliance with those requirements.
We do not believe that sources and
states should be limited to Federal
Register test methods for developing
their emissions inventories, for
developing applicable requirements,
and for demonstrating compliance with
applicable requirements. Accordingly,
we believe that it is appropriate for
sources and states to use other test
methods, even if there is a Federal
Register test method, as long as the test
method used is a reliable indicator of
the emissions performance for the
regulated pollutant.
d. Comments on Air Quality Models
Comment:
Commenters supporting EPA’s
proposal to repeal the grandfather
provision generally believe that
sufficient modeling tools are available to
complete a PM2.5 analysis. One local
agency commenter states that air quality
modeling of direct PM2.5 emissions is
readily available using EPA-approved
models.
The same commenter also claims that
several states (New York, New Jersey,
Connecticut) have developed policies by
which permit applicants use standard
modeling techniques to propose permit
limits on PM2.5 emissions that would
not cause or contribute to an exceedance
of the PM2.5 NAAQS. The commenter
acknowledges the present difficulty in
modeling secondary PM2.5 emissions,
but points out that this does not
preclude a permit applicant from
determining whether the direct
emissions of PM2.5 from the proposed
source or modification will cause or
contribute to a violation of the NAAQS.
An environmental group commenter
similarly agrees with EPA’s conclusion
that the challenges related to modeling
are not a valid basis for using PM10 as
a surrogate.
Other commenters, however, express
concern about the lack of adequate
modeling techniques to fully address
the PM2.5 impacts resulting from both
direct PM2.5 emissions and PM2.5
precursors. One commenter describes
current problems associated with trying
to model the impacts of PM2.5
precursors and expresses concern that
by not including formation of PM2.5
from precursor emissions, the complete
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impact cannot be assessed. Another
commenter acknowledges that the air
quality dispersion model, AERMOD,
can accurately estimate the impact of
direct PM2.5 emissions, but believes that
this is inadequate because elevated
ground level readings of PM2.5 seem to
have little to do with local direct PM2.5
emissions, but instead result from
several days of stagnating atmospheric
conditions that lead to the build-up of
secondary nitrates and sulfates in the
air. The commenter points out that
AERMOD does not address the chemical
transformations that lead to the creation
of these nitrates and sulfates from
precursor emissions.
Response:
We agree with the commenters who
indicate that our proposal to repeal the
grandfather provision should be
finalized despite the technical
difficulties with estimating the impacts
from emissions of PM2.5 precursors. We
acknowledge that current modeling
techniques do not adequately account
for the secondarily-formed ambient
impacts of PM2.5 caused by PM2.5
precursors. We are currently working on
techniques to address such deficiencies
in order to improve the ability to
estimate overall impacts of PM2.5 against
the NAAQS and upcoming increments.
Nevertheless, models are available to
model the ambient impact of direct
PM2.5 emissions, and we believe that it
is reasonable to carry out the required
air quality impact analyses with these
models. In a March 23, 2010, EPA
modeling guidance memorandum titled,
‘‘Modeling Procedures for
Demonstrating Compliance with PM2.5
NAAQS,’’ we provided procedures that
enable an applicant to complete both a
preliminary significant impact analysis
and a cumulative impact analysis to
determine the impact of a PSD source or
modification on the PM2.5 NAAQS.18
The guidance memorandum refers to the
recommended procedures as a
screening-level analysis or a ‘‘First Tier
modeling analysis’’ for demonstrating
compliance with PM2.5 NAAQS and
increments. The guidance memorandum
acknowledges that techniques for
modeling the individual source
contributions to secondary formation of
PM2.5 from precursor emissions are not
currently provided for within EPA’s
‘‘Guideline on Air Quality Models’’ (also
published as Appendix W of 40 CFR
part 51). However, the March 2010
guideline memorandum provides
procedures to account for the secondary
contribution from regional and local
sources of precursor emissions as part of
the cumulative impact analysis for
18 https://www.epa.gov/ttn/scram.
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appropriate comparison to the annual
and daily PM2.5 NAAQS through the use
of monitored background ambient
concentrations. We are planning to
provide additional guidance on PM2.5
modeling for PSD permitting that will
include more details on conducting
such modeling, including options to
enable more complete accounting for
individual source contributions to
secondary PM2.5 formation when their
precursor emissions are sufficient to
warrant inclusion. Therefore, we believe
that the tools and models now available
to address direct PM2.5 emissions, and to
a lesser extent secondarily-formed
PM2.5, are in total sufficient, along with
our other reasons provided in this
preamble, to support our conclusion
that it is appropriate to repeal the
grandfather provision for PM2.5, thereby
ending the use of the 1997 PM10
Surrogate Policy under the Federal PSD
program.
52.21(b)(13) and (14), any major source
that commences construction after the
major source baseline date consumes
increment, which will be the case for
any source that receives its permit after
that date.) We stated further that, while
EPA will not require any such source to
include a PM2.5 increment analysis as
part of its initial PSD application, an
increment analysis ultimately will be
required before the permit may be
issued if the date of issuance will occur
after October 20, 2011 (the trigger date
for the PM2.5 increment), when the
PM2.5 increments can be triggered under
the Federal PSD program. See 74 FR
64899. Any formerly grandfathered
source that has not yet received its final
permit will be subject to the same
transition provisions for PM2.5
increments.
D. What final action is EPA taking on
the grandfather provision for PM2.5?
We have decided to repeal the
6. Comments on the Lack of Key PM2.5
grandfather provision for PM2.5
Implementation Requirements
contained in the Federal PSD program at
40 CFR 52.21(i)(1)(xi). As the result of
Comment:
Several state agency, state/local
this final action, any PSD permit
agency association, private citizen, and
application previously covered by the
industry commenters oppose EPA’s
grandfather provision that is not issued
proposed repeal of the grandfather
a final and effective PSD permit before
provision because EPA has yet to take
the effective date of this rule will not be
final action under 40 CFR 51.166 and
able to rely on the 1997 PM10 Surrogate
52.21 to address key parameters needed Policy to satisfy the PSD requirements
to implement the PSD permit program
for PM2.5. Unless the application
for PM2.5. The key parameters include
includes a valid surrogacy
SILs, an SMC, and increments for PM2.5. demonstration (i.e., the applicant can
Response:
show that meeting the requirements for
On October 20, 2010, we promulgated PM10 will also meet the requirements for
a final rule at 75 FR 64864 that contains PM2.5), the application will need to
the PM2.5 increments, SILs, and SMC.
contain PM2.5 data and analyses to meet
Under that rule, the SILs and SMC
the PM2.5 requirements to ensure that
became effective in the Federal PSD
the applicable administrative record for
program as of December 20, 2010, and
the permit application is sufficient to
the PM2.5 increments will become
demonstrate compliance with those
effective on October 20, 2011. Thus,
requirements. Such requirements
under the Federal program there is no
include the analyses necessary to (1)
longer cause for the commenters’
establish the appropriate BACT
concern that implementation of PSD for emissions limitation(s) for PM2.5 in the
PM2.5 will be difficult and burdensome
permit, as required by section 165(a)(4)
due to the absence of the screening
of the Act, and (2) demonstrate that the
levels embodied in the SILs and SMC.
emissions increase from the proposed
There will be some period after the
new or modified major stationary source
repeal of the grandfather provision
will not cause or contribute to a
under this final rule before the PM2.5
violation of the PM2.5 NAAQS, as
increments become effective. However,
required by section 165(a)(3) of the Act.
note that in the preamble to the October For any application that previously was
20, 2010, final rule for PM2.5 increments, relying completely on a PM10 surrogate
SILs, and SMC we stated that under that analysis based solely on the 1997 PM10
rule, sources applying for a PSD permit
Surrogate Policy, additional information
under the Federal PSD program after the will be required to fulfill these
major source baseline date for PM2.5
requirements.
The EPA is aware of 27 sources that
(i.e., after October 20, 2010), but before
had submitted PSD permit applications
the PM2.5 increments become effective
under the Federal PSD program prior to
(i.e., before October 20, 2011), will be
considered to consume PM2.5 increment. July 15, 2008—the effective date of the
(Under section 169(4) of the Act and the 2008 PM2.5 NSR Implementation Rule—
implementing regulations at 40 CFR
but did not receive their permits by that
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Federal Register / Vol. 76, No. 96 / Wednesday, May 18, 2011 / Rules and Regulations
date. While some of these applicants for
PSD permits have already sought
alternative means of obtaining the
necessary permit, those that have not
yet done so will be required to provide
a PM2.5 analysis that demonstrates the
application of BACT and that the
source’s emissions will not cause or
contribute to a violation of the PM2.5
NAAQS or use a surrogate approach, as
long as that approach comports with the
conditions set forth by previous court
determinations concerning surrogacy
demonstrations. This final rule ensures
that the 1997 PM10 Surrogate Policy will
no longer be applicable to satisfy the
PSD requirements for PM2.5 under the
Federal PSD program.
V. What action is EPA taking on the
1997 PM10 Surrogate Policy for state
PSD programs?
On February 11, 2010, EPA proposed
to end the 1997 PM10 Surrogate Policy
in SIP-approved states before May 16,
2008. In that notice, EPA described the
current status of the 1997 PM10
Surrogate Policy under state PSD
programs that are part of an approved
SIP, and explained why EPA was
proposing to end the use of the 1997
PM10 Surrogate Policy early. 75 FR
6833–34 (Feb. 11, 2010). As indicated
above, EPA in this Federal Register
notice is taking no action concerning its
proposal to end early the use of the 1997
PM10 Surrogate Policy under state PSD
programs that are part of an approved
SIP. Accordingly, the use of the 1997
PM10 Surrogate Policy under such state
programs will end on May 16, 2011, in
accordance with the discussion in the
May 16, 2008, preamble. 73 FR 28321,
at 28340–41.
VI. Statutory and Executive Order
Reviews
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A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735, October 4, 1993), this action is a
‘‘significant regulatory action’’ because it
raises novel legal or policy issues.
Accordingly, EPA submitted this action
to the Office of Management and Budget
(OMB) for review under Executive
Order 12866 and any changes made in
response to OMB recommendations
have been documented in the docket for
this action.
B. Paperwork Reduction Act
This action does not impose any new
information collection burden that is
not already accounted for in the
approved information collection request
(ICR) for the NSR program. We are not
adding any new paperwork
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requirements (e.g., monitoring,
reporting, and recordkeeping) as part of
this final action. This action amends
one part of the regulations at 40 CFR
52.21 by repealing the grandfather
provision that affects fewer than 30
sources. However, the approved ICR for
the NSR program was prepared as if the
2008 PM2.5 NSR Implementation Rule,
which added PM2.5 to the NSR program,
would be fully implemented
immediately upon the effective date of
the rule without any phase-in period
during which either the grandfather
provision or 1997 PM10 Surrogate Policy
would apply. Thus, while this action
will result in increased permitting
burden for those sources who would
have otherwise been able to use the
grandfather provision or 1997 PM10
Surrogate Policy, this burden is already
included in the approved ICR. The OMB
previously approved the information
collection requirements contained in the
existing regulations (40 CFR parts 51
and 52) under the provisions of the
Paperwork Reduction Act, 44 U.S.C.
3501 et seq., and assigned OMB control
number 2060–0003. The OMB control
numbers for EPA’s regulations in 40
CFR are listed in 40 CFR part 9.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice-and-comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute unless the agency certifies
that the rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small
organizations, and small governmental
jurisdictions.
For purposes of assessing the impacts
of this final rule on small entities, small
entity is defined as: (1) A small business
as defined by the Small Business
Administration’s regulations at 13 CFR
121.201; (2) a small governmental
jurisdiction that is a government of a
city, county, town, school district or
special district with a population of less
than 50,000; and (3) a small
organization that is any not-for-profit
enterprise which is independently
owned and operated and is not
dominant in its field.
After considering the economic
impacts of this final rule on small
entities, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
This final rule will not impose any new
requirements or burdens on small
entities. We have determined that small
entities will not incur any adverse
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28659
impacts as a result of this action to
amend the regulations at 40 CFR 52.21
(by repealing the grandfather provision
that affects fewer than 30 sources).
Small businesses and other small
entities generally are not subject to the
PSD program, which applies only to
new major stationary sources and major
modifications at existing major
stationary sources. In addition, we do
not believe that any small governments
serve as PSD reviewing authorities.
D. Unfunded Mandates Reform Act
This rule does not contain a Federal
mandate that may result in expenditures
of $100 million or more for state, local,
and tribal governments, in the aggregate,
or the private sector in any 1 year. This
action only amends one part of the
regulations at 40 CFR 52.21 by repealing
the grandfather provision that affects
fewer than 30 sources. Therefore, this
action is not subject to the requirements
of sections 202 or 205 of UMRA.
This action is also not subject to the
requirements of section 203 of UMRA
because it contains no regulatory
requirements that might significantly or
uniquely affect small governments. This
final rule applies only to new major
stationary sources and to major
modifications at existing major
stationary sources, and we have no
indication that small governments own
or operate any major sources that are
potentially affected by this action. In
addition, we do not believe that any
small governments serve as PSD
reviewing authorities.
E. Executive Order 13132: Federalism
This action does not have federalism
implications. It will not have substantial
direct effects on the states, on the
relationship between the national
government and the states, or on the
distribution of power and
responsibilities among the various
levels of government as specified in
Executive Order 13132. This action only
amends one part of the regulations at 40
CFR 52.21 by repealing the grandfather
provision for PM2.5 that affects fewer
than 30 sources. Thus, Executive Order
13132 does not apply to this final rule.
In the spirit of Executive Order 13132,
and consistent with EPA policy to
promote communications between EPA
and state and local governments, EPA
specifically solicited comment on the
proposed rule from state and local
officials. We received comments from
11 state/local regulatory agency and
regulatory agency association
commenters concerning the proposed
repeal of the grandfather provision
under the Federal PSD program and the
early end of the 1997 PM10 Surrogate
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Federal Register / Vol. 76, No. 96 / Wednesday, May 18, 2011 / Rules and Regulations
Policy under SIP-approved state PSD
programs. The comments pertaining to
our repeal of the grandfather provision
are summarized and addressed in this
preamble and in a Technical Support
Document in the Docket for this
rulemaking.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This action does not have tribal
implications, as specified in Executive
Order 13175 (65 FR 67249, November 9,
2000). This action will not impose any
new obligations or enforceable duties on
tribal governments. Thus, Executive
Order 13175 does not apply to this
action.
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
The EPA interprets Executive Order
13045 (62 FR 19885, April 23, 1997) as
applying only to those regulatory
actions that concern health or safety
risks, such that the analysis required
under section 5–501 of the Executive
Order has the potential to influence the
regulation. This action is not subject to
Executive Order 13045 because it does
not establish an environmental standard
intended to mitigate health or safety
risks. In fact, this action will help
ensure that the health-based national
standards for PM2.5 are adequately
protected against the adverse effects of
PM2.5 emissions from new and modified
sources of air pollution by ending the
use of the 1997 PM10 Surrogate Policy
as a substitute approach for satisfying
the PM2.5 requirements under the
Federal PSD program.
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H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not subject to Executive
Order 13211 (66 FR 28355 (May 22,
2001)), because it is not a significant
regulatory action under Executive Order
12866. The EPA is amending one part of
the regulations at 40 CFR 52.21
(expected to affect fewer than 30
regulated entities). Only a portion of the
sources involved in the production or
distribution of energy could be
impacted.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law No.
104–113, 12(d) (15 U.S.C. 272 note)
directs EPA to use voluntary consensus
standards in its regulatory activities
unless to do so would be inconsistent
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with applicable law or otherwise
impractical. Voluntary consensus
standards are technical standards (e.g.,
materials specifications, test methods,
sampling procedures, and business
practices) that are developed or adopted
by voluntary consensus standards
bodies. The NTTAA directs EPA to
provide Congress, through OMB,
explanations when the Agency decides
not to use available and applicable
voluntary consensus standards.
This action does not involve technical
standards. Therefore, EPA did not
consider the use of any voluntary
consensus standards.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 12898 (59 FR 7629
(Feb. 16, 1994)) establishes Federal
executive policy on environmental
justice. Its main provision directs
Federal agencies, to the greatest extent
practicable and permitted by law, to
make environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
The EPA has concluded that this final
rule does not result in
disproportionately high and adverse
human health or environmental effects
on minority and/or low income
populations. The rule only amends one
part of the regulations at 40 CFR 52.21
by repealing the grandfather provision
that affects fewer than 30 sources. The
affected sources, after further analysis
and data collection, may receive
permitted emissions limits that are
equally or more protective of public
health than would be likely in the
absence of this final rule.
K. Congressional Review Act
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. The EPA will
submit a report containing this rule 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
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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). This rule will be effective on
July 18, 2011.
L. Conclusion and Determination Under
Section 307(d)
Pursuant to section 307(d)(1)(J) of the
CAA, this action is subject to the
provisions of section 307(d). Further, to
the extent that any aspects of this rule
are not subject to the provisions of
section 307(d) pursuant to section
307(d)(1)(J), the Administrator
determines that this rule is subject to
the provisions of section 307(d)
pursuant to section 307(d)(1)(V).
VII. Judicial Review
Under section 307(b)(1) of the Act,
petitions for judicial review of this
action must be filed in the United States
Court of Appeals for the District of
Columbia Circuit by July 18, 2011. Any
such judicial review is limited to only
those objections that are raised with
reasonable specificity in timely
comments. Filing a petition for
reconsideration by the Administrator of
this final rule does not affect the finality
of this rule 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. Under section 307(b)(2) of the
Act, the requirements of this final action
may not be challenged later in civil or
criminal proceedings brought by us to
enforce these requirements.
VIII. Statutory Authority
The statutory authority for this action
is provided by the CAA, as amended (42
U.S.C. 7401 et seq.). Relevant portions
of the Act include, but are not
necessarily limited to, sections 101, 110,
165, and 301 of the CAA as amended
(42 U.S.C. 7401, 7410, 7475, and 7601).
This action is also subject to section
307(d) of the Act (42 U.S.C. 7607(d)).
List of Subjects in 40 CFR Part 52
Administrative practices and
procedures, Air pollution control,
Environmental protection, Incorporation
by reference, Intergovernmental
relations.
Dated: May 10, 2011.
Lisa P. Jackson,
Administrator.
For the reasons set out in the
preamble, title 40, chapter I of the Code
of Federal Regulations is amended as
follows:
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Federal Register / Vol. 76, No. 96 / Wednesday, May 18, 2011 / Rules and Regulations
PART 52—[AMENDED]
1. The authority citation for part 52
continues to read as follows:
■
Authority: 42 U.S.C. 7401, et seq.
§ 52.21
[Amended]
2. In § 52.21, remove paragraph
(i)(1)(xi).
■
[FR Doc. 2011–12089 Filed 5–17–11; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R09–OAR–2011–0372; FRL–9307–3]
Interim Final Determination To Defer
Sanctions, Sacramento Metro 1-Hour
Ozone Nonattainment Area, California
Environmental Protection
Agency (EPA).
ACTION: Interim final rule.
AGENCY:
EPA is making an interim
final determination to defer imposition
of sanctions based on a proposed
determination, published elsewhere in
this Federal Register, that the State of
California is no longer required to
submit or implement a Clean Air Act
(CAA) Section 185 fee program
(Termination Determination) for the
Sacramento Metro 1-hour Ozone
nonattainment area (Sacramento Metro
Area) to satisfy anti-backsliding
requirements for the 1-hour Ozone
standard.
SUMMARY:
This interim final determination
is effective on May 18, 2011. However,
comments will be accepted until June
17, 2011.
ADDRESSES: Submit comments,
identified by docket number EPA–R09–
OAR–2011–0372, by one of the
following methods:
1. Federal eRulemaking Portal: https://
www.regulations.gov. Follow the on-line
instructions.
2. E-mail: steckel.andrew@epa.gov.
3. Mail or deliver: Andrew Steckel
(Air–4), U.S. Environmental Protection
Agency Region IX, 75 Hawthorne Street,
San Francisco, CA 94105–3901.
Instructions: All comments will be
included in the public docket without
change and may be made available
online at https://www.regulations.gov,
including any personal information
provided, unless the comment includes
Confidential Business Information (CBI)
or other information whose disclosure is
restricted by statute. Information that
you consider CBI or otherwise protected
should be clearly identified as such and
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DATES:
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should not be submitted through https://
www.regulations.gov or e-mail. https://
www.regulations.gov is an ‘‘anonymous
access’’ system, and EPA will not know
your identity or contact information
unless you provide it in the body of
your comment. If you send e-mail
directly to EPA, your e-mail address
will be automatically captured and
included as part of the public comment.
If EPA cannot read your comment due
to technical difficulties and cannot
contact you for clarification, EPA may
not be able to consider your comment.
Docket: Generally, documents in the
docket for this action are available
electronically at https://
www.regulations.gov and in hard copy
at EPA Region IX, 75 Hawthorne Street,
San Francisco, California. While all
documents in the docket are listed at
https://www.regulations.gov, some
information may be publicly available
only at the hard copy location (e.g.,
copyrighted material, large maps), and
some may not be publicly available in
either location (e.g., CBI). To inspect the
hard copy materials, please schedule an
appointment during normal business
hours with the contact listed in the FOR
FURTHER INFORMATION CONTACT section.
FOR FURTHER INFORMATION CONTACT: Lily
Wong, EPA Region IX, (415) 947–4114,
wong.lily@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document, ‘‘we,’’ ‘‘us’’
and ‘‘our’’ refer to EPA.
I. Background
On January 5, 2010 (75 FR 232), we
published a finding that the State of
California failed to submit State
Implementation Plans (SIPs) to satisfy
CAA section 185 for three 1-hour Ozone
nonattainment areas: Sacramento Metro
Area, Southeast Desert, and Los
Angeles-South Coast Air Basin. As
discussed in our January 2010 action,
the finding regarding the Sacramento
Metro Area addressed the Yolo/Solano
Air Quality Management District,
Feather River Air Quality Management
District, Placer County Air Pollution
Control District and El Dorado County
Air Quality Management District. It did
not address the Sacramento
Metropolitan Air Quality Management
District. This finding started a sanctions
clock for imposition of offset sanctions
18 months after January 5, 2010 and
highway sanctions 6 months later,
pursuant to section 179 of the CAA and
our regulations at 40 CFR 52.31.
On July 7, 2010 and in an update on
April 13, 2011, the California Air
Resources Board (CARB) submitted a
request that EPA determine that the
CAA section 185 obligation has been
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terminated for the Sacramento Metro
Area. This termination determination
request was supported by data
demonstrating that the Sacramento
Metro Area has attained the 1-hour
Ozone standard based on the most
recent three years of complete, qualityassured and certified data (2007–2009),
and that the improvement in air quality
resulted from permanent and
enforceable emissions reductions. In the
Proposed Rules section of today’s
Federal Register, we have proposed
approval of this submittal. Based on
today’s proposed approval, we are
taking this final rulemaking action,
effective on publication, to defer
imposition of sanctions that were
triggered by our January 5, 2010 finding
of failure to submit for the Sacramento
Metro Area based on a finding that it is
more likely than not that the
Sacramento Metro Area is no longer
obligated to submit a 185 program.
EPA is providing the public with an
opportunity to comment on this deferral
of sanctions. If comments are submitted
that change our assessment described in
this final determination and the
proposed CAA section 185 termination
determination for the Sacramento Metro
Area, we would take final action
proposing to deny or denying the
termination determination request and
lifting this deferral of the sanctions. If
no comments are submitted that change
our assessment, then with regard to the
finding of failure to submit discussed
previously, any imposed sanctions
would no longer apply and any sanction
clocks would be permanently
terminated on the effective date of a
final CAA section 185 termination
determination.
II. EPA Action
We are making an interim final
determination to defer CAA section 179
sanctions associated with the
Sacramento Metro Area’s 1-hour Ozone
CAA section 185 obligation based on
our concurrent proposal to approve a
CAA section 185 termination
determination which would remove the
obligation of the state to submit a
section 185 SIP when finalized.
Because EPA has preliminarily
determined that the State is not
obligated to submit the SIP that was the
basis of EPA’s finding of failure to
submit, relief from sanctions should be
provided as quickly as possible.
Therefore, EPA is invoking the good
cause exception under the
Administrative Procedure Act (APA) in
not providing an opportunity for
comment before this action takes effect
(5 U.S.C. 553(b)(3)). However, by this
action EPA is providing the public with
E:\FR\FM\18MYR1.SGM
18MYR1
Agencies
[Federal Register Volume 76, Number 96 (Wednesday, May 18, 2011)]
[Rules and Regulations]
[Pages 28646-28661]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-12089]
=======================================================================
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-HQ-OAR-2003-0062: FRL-9306-9]
RIN 2060-AP75
Implementation of the New Source Review (NSR) Program for
Particulate Matter Less Than 2.5 Micrometers (PM2.5); Final
Rule To Repeal Grandfather Provision
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
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SUMMARY: The EPA is issuing a final rule that repeals the
``grandfather'' provision for particulate matter less than 2.5
micrometers (PM2.5) under the Federal Prevention of
Significant Deterioration (PSD) permit program, which is administered
by EPA in states that lack a PSD permit program in their approved state
implementation plan (SIP). The grandfather provision allowed certain
facilities under certain circumstances to satisfy the PSD permit
program requirements for PM2.5 by meeting the requirements
for controlling particulate matter less than 10 micrometers
(PM10) and analyzing impacts on PM10 air quality
as a surrogate approach based on an EPA policy known as the ``1997
PM10 Surrogate Policy.'' In its February 11, 2010, notice of
proposed rulemaking, EPA also proposed to end early the 1997
PM10 Surrogate Policy in EPA-approved state PSD programs
during the remainder of the SIP development period, which ends on May
16, 2011. EPA is taking no final action on that aspect of the proposal.
DATES: This final rule is effective on July 18, 2011.
ADDRESSES: The EPA has established a docket for this action under
Docket ID No. EPA-HQ-OAR-2003-0062. All documents in the docket are
listed on the https://www.regulations.gov Web site. Although listed in
the index, some information may not be publicly available, e.g.,
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Certain other material, such as
copyrighted material, is not placed on the Internet and will be
publicly available only in hard copy form. Publicly available docket
materials are available either electronically through https://www.regulations.gov or in hard copy at the Air Docket, EPA/DC, EPA
West, Room 3334, 1301 Constitution Avenue, Northwest, Washington, DC.
The Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding legal holidays. The telephone number for the
Public Reading Room is (202) 566-1744, and the telephone number for the
Air Docket is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: Mr. Dan deRoeck, Air Quality Policy
Division, (C504-03), U.S. Environmental Protection Agency, Research
Triangle Park, NC, 27711; telephone number (919) 541-5593; fax number
(919) 541-5509; or e-mail address: deroeck.dan@epa.gov.
SUPPLEMENTARY INFORMATION: The information in this Supplementary
Information section of this preamble is organized as follows:
I. General Information
A. Does this action apply to me?
B. Where can I get a copy of this document and other related
information?
II. Overview of This Final Rule
III. Background
A. Prevention of Significant Deterioration Program
B. Fine PM and the NAAQS for PM2.5
C. How is the PSD program for PM2.5 implemented?
IV. Grandfather Provision for PM2.5 in the Federal PSD
Program
A. What is the grandfather provision for PM2.5?
B. Why did EPA propose to repeal the grandfather provision for
PM2.5?
C. Summary of Comments and Responses on the Proposed Repeal of
the Grandfather Provision
D. What final action is EPA taking on the grandfather provision
for PM2.5?
V. What action is EPA taking on the 1997 PM10 Surrogate
Policy for state PSD programs?
VI. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health and Safety Risks
H. Executive Order 13211: Actions That Significantly Affect
Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
J. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low-Income
Populations
K. Congressional Review Act
L. Conclusion and Determination Under Section 307(d)
VII. Judicial Review
VIII. Statutory Authority
[[Page 28647]]
I. General Information
A. Does this action apply to me?
Entities potentially affected by this action include those proposed
new and modified major stationary sources subject to the Federal PSD
program that submitted a complete application for a PSD permit before
the July 15, 2008, effective date of the final PM2.5 New
Source Review (NSR) Implementation Rule (73 FR 28321), but have not yet
received a final and effective permit authorizing the source to
commence construction.
The EPA estimates that fewer than 30 proposed new major sources or
modifications will be affected by the repeal of the grandfather
provision in the Federal PSD program. At least two projects known to
have been grandfathered received final permits to construct (that are
effective) prior to EPA taking action to stay the provision in June
2009; EPA's final action to repeal the grandfather provision does not
apply retroactively to such permits.
The majority of sources potentially affected are expected to be in
the following groups:
------------------------------------------------------------------------
Industry group NAICS \a\
------------------------------------------------------------------------
Electric services...................... 221111, 221112, 221113, 221119,
221121, 221122.
Petroleum refining..................... 32411.
Industrial inorganic chemicals......... 325181, 32512, 325131, 325182,
211112, 325998, 331311,
325188.
Industrial organic chemicals........... 32511, 325132, 325192, 325188,
325193, 32512, 325199.
Miscellaneous chemical products........ 32552, 32592, 32591, 325182,
32551.
Natural gas liquids.................... 211112.
Natural gas transport.................. 48621, 22121.
Pulp and paper mills................... 32211, 322121, 322122, 32213.
Paper mills............................ 322121, 322122.
Automobile manufacturing............... 336111, 336112, 336712, 336211,
336992, 336322, 336312, 33633,
33634, 33635, 336399, 336212,
336213.
Pharmaceuticals........................ 325411, 325412, 325413, 325414.
------------------------------------------------------------------------
\a\ North American Industry Classification System.
Entities affected by this action also include state and local
governments responsible for implementing PSD pre-construction permit
programs for new and modified major stationary sources under the
Federal PSD permit program (40 CFR 52.21).
B. Where can I get a copy of this document and other related
information?
In addition to being available in the docket, an electronic copy of
this final rule will also be available on the World Wide Web. Following
signature by the EPA Administrator, a copy of this final rule will be
posted in the regulations and standards section of our NSR home page
located at https://www.epa.gov/nsr.
II. Overview of This Final Rule
In this final rule we \1\ are taking final action on one of the two
actions that we proposed in a notice of proposed rulemaking on February
11, 2010, at 75 FR 6827. We are taking final action on the proposal to
repeal the grandfather provision for PM2.5 contained in the
Federal PSD rules at 40 CFR 52.21(i)(1)(xi). The grandfather provision,
applicable only to PSD source applications that were determined to be
complete before July 15, 2008, enabled those applications to continue
to be reviewed for PM10 (i.e., the 1997 PM10
Surrogate Policy) in lieu of the new requirements for PM2.5,
which became effective on July 15, 2008.
---------------------------------------------------------------------------
\1\ In this preamble, the terms ``we,'' ``us,'' and ``our''
refer to the EPA.
---------------------------------------------------------------------------
When EPA issued the PM10 Surrogate Policy in 1997, the
policy enabled sources, EPA, and state and local permitting authorities
to address the PSD requirements for PM2.5 simply by
satisfying the requirements for PM10--a regulated form of
particulate matter (PM) that includes PM2.5 as well as
larger particles. As explained in the 1997 PM10 Surrogate
Policy, some alternative to directly addressing PM2.5 was
necessary at that time because of various technical problems that made
it infeasible to estimate PM2.5 and conduct the analyses
necessary to demonstrate compliance with the applicable
PM2.5 requirements under the PSD program as required by
section 165 of the Clean Air Act (CAA or Act).
More recently, EPA has made important progress in addressing the
technical issues that impeded a PM2.5 analysis. With the
deployment and operation of the monitoring network for PM2.5
beginning in 1999, ambient air quality monitoring data has become more
abundantly available. Also, EPA has promulgated screening tools,
including a significant emissions rate (SER), significant impact levels
(SILs), and a significant monitoring concentration (SMC) to streamline
the implementation of the PSD program for PM2.5. Finally,
EPA has issued revised test methods for sampling emissions of
PM2.5 and its condensable fraction, and issued interim
modeling guidance for modeling PM2.5 emissions to complete a
cumulative air quality analysis for PM2.5.
Accordingly, in this final action, EPA will end the use of the 1997
PM10 Surrogate Policy for PSD permits under the Federal PSD
program (40 CFR 52.21) for sources that have been covered by the
grandfather provision (that is, those sources for which a complete
permit application was submitted before July 15, 2008 \2\) and that
have not yet been issued a permit by the effective date of this final
rule. After this final rule becomes effective, in order for those
permits to be issued, such applications will have to be reviewed
directly against the PM2.5 requirements or, alternatively,
use a surrogate approach for PM2.5 (other than the 1997
PM10 Surrogate Policy) that is consistent with the
applicable case law. Thus, those affected PSD permit applications must
be amended to include further analyses to demonstrate compliance with
the PSD requirements for PM2.5. Alternatively, those
affected PSD permit applications must show that PM10 is an
adequate surrogate for PM2.5 for that specific project. The
demonstration must show, at a minimum, that the source's emissions are
controlled to a level that satisfies Best Available Control Technology
(BACT) requirements for PM2.5 and that the emissions will
not cause or contribute to a violation of any National Ambient Air
Quality Standard (NAAQS or standard) for PM2.5.
---------------------------------------------------------------------------
\2\ Sources that applied for a PSD permit under the Federal PSD
program on or after July 15, 2008, are already excluded from using
the 1997 PM10 Surrogate Policy as a means of satisfying
the PSD requirements for PM2.5. See 73 FR 28321.
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[[Page 28648]]
We believe that it is appropriate to terminate the use of the 1997
PM10 Surrogate Policy at this time for those PSD
applications grandfathered under the Federal PSD program because the
necessary technical tools to conduct PM2.5 analyses for PSD
sources are now available. The 1997 PM10 Surrogate Policy
was always intended as an interim measure that was to remain in effect
only as long as needed. Over the past 13 years, EPA believes that the
necessary technical tools and test methods required to show compliance
with PM2.5 have been developed and, hence, we believe that
the need for this interim approach no longer exists.
We do not believe that the use of the 1997 PM10
Surrogate Policy affords the same degree of protection of the
PM2.5 NAAQS from major new and modified stationary sources
as does the direct analysis of PM2.5 emissions. In addition
to the fact that the original PM2.5 NAAQS promulgated in
1997 were generally more stringent than the corresponding
PM10 NAAQS, the strengthening of the 24-hour primary
PM2.5 NAAQS in 2005 created a greater disparity between the
relative stringency of the PM2.5 and PM10
standards. Thus, now that the necessary technical tools are available,
we believe that it is important to move as quickly as possible to
implement fully the PSD program for PM2.5.
We recognize that this action will in some cases increase the PSD
permit review timeframe (although not unexpectedly) for the affected
grandfathered sources, but we believe that the use of the 1997
PM10 Surrogate Policy should be permanently discontinued
under the Federal PSD program. Those grandfathered sources with pending
permits have been on notice since June 1, 2009, (the date of our
Federal Register notice announcing that we had agreed to reconsider the
grandfather provision and to administratively stay the provision so
that we could propose repealing it) that EPA was considering ending the
grandfather provision for PM2.5 and, as noted above, now
have additional technical tools to complete the permitting process for
PM2.5.
In our February 2010 proposed rule, we also proposed to end the use
of the 1997 PM10 Surrogate Policy for permits issued under
PSD programs implemented by states as part of their approved SIP. We
received and have reviewed some comments that support an early end to
the policy and some comments that oppose ending the policy earlier than
the original May 16, 2011, sunset date. Some of the opposing comments
also asked EPA to extend the time that the policy could be used beyond
the original sunset date. At this time, however, we are taking no
action on our proposal to end the use of the 1997 PM10
Surrogate Policy or to otherwise change the time period during which
the policy could continue to be used.
Thus, as announced in the May 2008 rulemaking, the 1997
PM10 Surrogate Policy may not be used for any state PSD
permits after the 3 years allowed for SIP development (ending May 16,
2011). With the end of the 1997 PM10 Surrogate Policy in
SIP-approved states on May 16, 2011, and the repeal of the grandfather
provision in this final action, the 1997 PM10 Surrogate
Policy may not be relied on for any pending or future applications.
III. Background
A. Prevention of Significant Deterioration Program
The NSR provisions of the Act are a combination of air quality
planning and air pollution control technology program requirements for
new and modified major stationary sources of air pollution. Section 109
of the Act requires EPA to promulgate primary NAAQS to protect public
health and secondary NAAQS to protect public welfare. Once we have set
these standards, states must develop, adopt, and submit to us for
approval SIPs that contain emission limitations and other control
measures to attain and maintain the NAAQS and to meet the other
requirements of section 110(a) of the Act.
Part C of title I of the Act contains the requirements for a
component of the major NSR program known as the PSD (short for
``Prevention of Significant Deterioration'') program. The PSD program
sets forth procedures for the preconstruction review and permitting of
new and modified major stationary sources of air pollution locating in
areas meeting the NAAQS (``attainment'' areas) and areas for which
there is insufficient information to classify an area as either
attainment or nonattainment (``unclassifiable'' areas). In most states,
EPA has approved a PSD permit program that is part of the applicable
SIP. The Federal PSD program at 40 CFR 52.21 applies in states that
lack a SIP-approved PSD permit program, and in Indian country.\3\ The
applicability of the PSD program to a new major stationary source or
major modification must be determined in advance of construction and is
a pollutant-specific determination. Once a major new source or major
modification is determined to be subject to the PSD program (i.e., to
be a ``PSD source''), among other requirements, it must undertake a
series of analyses for each regulated NSR pollutant subject to review
to demonstrate that it will use the BACT and will not cause or
contribute to a violation of any NAAQS or increment. In cases where the
source's emissions of any NSR regulated pollutant may adversely affect
an area specially classified as ``Class I,'' such as national parks and
wilderness areas, additional review must be conducted to protect the
Class I area's increments and special attributes referred to as ``air
quality related values.''
---------------------------------------------------------------------------
\3\ We have delegated our authority to some states that lack an
approved PSD program in their SIPs and have requested the authority
to implement the Federal PSD program. The EPA remains the reviewing
authority in non-delegated states lacking SIP-approved programs. The
current status of individual state PSD programs can be found at
EPA's Web site at https://www.epa.gov/nsr/where.html.
---------------------------------------------------------------------------
When the reviewing authority reaches a preliminary decision to
authorize construction of a proposed major new source or major
modification, the authority must provide notice of the preliminary
decision and an opportunity for comment by the general public,
industry, and other persons that may be affected by the emissions of
the proposed major source or major modification. After considering
these comments, the reviewing authority issues a final determination on
the construction permit in accordance with the PSD regulations.
However, under EPA regulations at 40 CFR part 124 and similar state
regulations, an administrative appeal of a permitting determination may
prevent the permit from becoming final and effective until the appeal
is resolved.
B. Fine PM and the NAAQS for PM2.5
Fine particles in the atmosphere are made up of a complex mixture
of components. Common constituents include sulfates; nitrates;
ammonium; elemental carbon; a great variety of organic compounds; and
inorganic material (including metals, dust, sea salt, and other trace
elements) generally referred to as ``crustal'' material, although it
may contain material from other sources. Airborne PM with a nominal
aerodynamic diameter of 2.5 micrometers or less (a micrometer is one-
millionth of a meter, and 2.5 micrometers is less than one-seventh the
average width of a human hair) is considered to be ``fine particles,''
and is also known as PM2.5. ``Primary'' particles are
emitted directly into the air as solid or liquid particles (e.g.,
elemental
[[Page 28649]]
carbon from diesel engines or fire activities, or condensable organic
particles from gasoline engines). ``Secondary'' particles (e.g.,
sulfates and nitrates) form in the atmosphere as a result of various
chemical reactions.
The health effects associated with exposure to PM2.5 are
significant and well studied. Epidemiological studies have shown a
significant correlation between elevated PM2.5 levels and
premature mortality. Other important effects associated with
PM2.5 exposure include aggravation of respiratory and
cardiovascular disease (as indicated by increased hospital admissions,
emergency room visits, absences from school or work, and restricted
activity days), lung disease, decreased lung function, asthma attacks,
and certain cardiovascular problems. Individuals particularly sensitive
to PM2.5 exposure include older adults, people with heart
and lung disease, and children.
The EPA has established primary health-based long-term and short-
term NAAQS for PM2.5. The long-term annual average standard
is 15 micrograms per cubic meter ([micro]g/m\3\), established in 1997.
See 62 FR 38652. The short-term 24-hour standard is 35 [micro]g/m\3\,
established in 2006. See 71 FR 61286. At the time we established the
primary standards in 1997, we also established welfare-based
(secondary) standards identical to the primary standards. The secondary
standards are designed to protect against major environmental effects
of PM2.5 such as visibility impairment, soiling, and
materials damage.
In addition, EPA has established a short-term primary and secondary
NAAQS for PM10 as an indicator for coarse PM. The short-term
standard for PM10 is 150 [micro]g/m\3\. See 71 FR 61236.
C. How is the PSD program for PM2.5 implemented?
After we promulgated the NAAQS for PM2.5 in 1997, we
issued a guidance document titled, ``Interim Implementation for the New
Source Review Requirements for PM2.5'' (John S. Seitz, EPA,
October 23, 1997).\4\ That guidance document, referred to throughout
this preamble as the ``1997 PM10 Surrogate Policy,'' allows
proposed major sources and major modifications to satisfy the PSD
requirements for PM2.5 by meeting the requirements for
controlling PM10 and for analyzing impacts on
PM10 air quality as a surrogate approach. The 1997
PM10 Surrogate Policy was designed to temporarily help
states implement the CAA requirements for PSD pertaining to the new
PM2.5 NAAQS and PM2.5 as a regulated pollutant.
We intended to make the policy available until we resolved the known
technical difficulties associated with addressing PM2.5.\5\
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\4\ Available in the docket for this rulemaking, ID No. EPA-HQ-
OAR-2003-0062, and at https://www.epa.gov/region07/programs/artd/air/nsr/nsrmemos/pm25.pdf.
\5\ We identified various technical difficulties, including the
lack of necessary tools to calculate the emissions of
PM2.5 and related precursors, the lack of adequate
modeling techniques to project ambient impacts, the lack of
PM2.5 monitoring sites, and the lack of adequate approved
test methods.
---------------------------------------------------------------------------
We believed the 1997 PM10 Surrogate Policy was necessary
because section 165(a)(1) of the Act provides that no new or modified
major source may be constructed without a PSD permit that meets all of
the section 165(a) requirements with respect to the regulated
pollutant. Moreover, section 165(a)(3) provides that the emissions from
any such source may not cause or contribute to a violation of ``any
NAAQS.'' The EPA policy for implementing the Federal PSD program
provides that the term ``any NAAQS'' applies to any existing NAAQS,
including new or revised NAAQS upon their effective date. Also, section
165(a)(4) requires BACT for each pollutant subject to PSD regulation.
PM2.5 became a regulated pollutant when EPA promulgated the
NAAQS for PM2.5 in 1997.
On November 1, 2005, we proposed the Clean Air Fine Particle
Implementation Rule (PM2.5 Implementation Rule) to implement
the 1997 PM2.5 NAAQS. See 70 FR 65984. The PM2.5
Implementation Rule proposal described the requirements that states and
tribes must meet in their implementation plans for attainment of the
PM2.5 NAAQS. Among other things, that rule proposal sought
comments on revisions to the NSR program in attainment and
unclassifiable areas (the PSD program), and in nonattainment areas (the
nonattainment NSR program).
For PSD, EPA proposed to revise the existing PSD rules in several
ways: by proposing a PSD major source threshold and SER for
PM2.5; proposing to define applicable precursors to regulate
under PSD and SERs for those precursors; proposing to clarify that
condensable PM2.5 must be included in determining major
source status; proposing options for implementing the preconstruction
monitoring requirements for PM2.5; and proposing transition
provisions for implementing the new PSD requirements for
PM2.5.
On September 21, 2007, EPA proposed additional program elements for
the PSD program for PM2.5 that were not included in the 2005
PM2.5 Implementation Rule proposal. The 2007 PSD proposal
included several options for defining the PM2.5 increments,
SILs, and an SMC for PM2.5. Increments define maximum
allowable increases in pollutant concentrations above a baseline
concentration for a particular area. The SILs and SMC are useful
screening tools for effectively implementing the air quality impact
requirements under PSD. See 72 FR 54112.
On May 16, 2008, EPA published a final PM2.5 NSR
Implementation Rule to complete the rulemaking for NSR based on the
2005 PM2.5 Implementation Rule proposal. The 2008
PM2.5 NSR Implementation Rule contains requirements for
state and tribal plans to implement the Act's preconstruction review
provisions for the PM2.5 NAAQS in both attainment and
nonattainment areas. See 73 FR 28321. The 2008 PM2.5 NSR
Implementation Rule generally requires that, as of the effective date
of the new rule (July 15, 2008), major stationary sources seeking
permits must begin directly satisfying the PM2.5
requirements, rather than relying on the 1997 PM10 Surrogate
Policy. In PM2.5 attainment (or unclassifiable) areas, the
new PSD requirements under 40 CFR 51.166 set forth the PM2.5
requirements for states with SIP-approved programs to include in their
state PSD programs; similar requirements were added to 40 CFR 52.21--
the Federal PSD program--for EPA (or, where applicable, delegated state
agencies) to use for implementing the new PM2.5 requirements
in states lacking approved PSD programs in their SIPs.
Although the 2008 PM2.5 NSR Implementation Rule
generally requires states to begin implementing the new
PM2.5 requirements upon the July 15, 2008, effective date of
the rule, EPA provided two transition provisions within the PSD program
under specific conditions. The first of these transition provisions, a
grandfather provision, applied specifically to certain sources that had
applied for PSD permits pursuant to the Federal PSD program under 40
CFR 52.21. The second transition provision allowed states to continue
using the 1997 PM10 Surrogate Policy on an interim basis to
implement the PM2.5 requirements in any state PSD program
that is part of an approved SIP. This latter exception was to apply to
permit reviews under state PSD programs until the end of the 3-year SIP
development period (which ends in May 2011) or until EPA approves the
revised state program, whichever comes first.
[[Page 28650]]
IV. Grandfather Provision for PM2.5 in the Federal PSD
Program
A. What is the grandfather provision for PM2.5?
Under certain circumstances, EPA has allowed proposed new major
sources and major modifications that have submitted a complete PSD
permit application before the effective date of an amendment to the PSD
regulations, but have not yet received a final and effective PSD
permit, to continue relying on information already in the application
rather than immediately having to amend applications to demonstrate
compliance with the new PSD requirements. In such a way, these proposed
sources and modifications were ``grandfathered'' or exempted from the
new PSD requirements that would otherwise have applied to them. For
example, the Federal PSD regulations at 40 CFR 52.21(i)(1)(x) provide
that the owners or operators of proposed sources or modifications that
submitted a complete permit application before July 31, 1987, (i.e.,
the effective date of the revisions to the Federal PSD regulations to
implement the PM10 NAAQS) are not required to meet the
requirements for PM10, but may instead satisfy the
requirements for total suspended particulate matter (TSP) that were
previously in effect.
In addition, EPA has allowed some grandfathering for permit
applications submitted before the effective date of an amendment to the
PSD regulations establishing new maximum allowable increases in
pollutant concentrations (also known as PSD increments). The Federal
PSD regulations at 40 CFR 52.21(i)(10) provide that proposed sources or
modifications that submitted a complete permit application before the
effective date of the increments for PM10 in the applicable
implementation plan are not required to meet the increment requirements
for PM10, but may instead satisfy the increment requirements
for TSP that were previously in effect. Also, 40 CFR 52.21(b)(i)(9)
provides that new sources or sources making modifications that
submitted complete permit applications before the provisions embodying
the maximum allowable increase for nitrogen oxides (the nitrogen
dioxide increments) took effect are not required to demonstrate
compliance with the new increment requirements to be eligible to
receive the permit.
Similarly, the 2008 PM2.5 NSR Implementation Rule added
a grandfather provision allowing permit applicants that had submitted a
complete application under the Federal PSD program at 40 CFR 52.21
prior to the July 15, 2008, effective date, but had not yet received
their PSD permit by that date, to continue being reviewed using the
1997 PM10 Surrogate Policy. The grandfather provision for
PM2.5, added as new paragraph (xi) to 40 CFR 52.21(i)(1),
was not proposed for notice and comment in the 2005 PM2.5
Implementation Rule proposal. Instead, the 2005 PM2.5
Implementation Rule proposal had provided that when we issued the final
rule, the new PM2.5 requirements would take effect
immediately in PSD permits issued in states where the Federal PSD
program applies. See 70 FR 65986 at 66043.
As described more in the discussion that follows in section IV.B of
this preamble, EPA has twice stayed the grandfather provision for
PM2.5, with the first of the two stays beginning on June 1,
2009. Consequently, permits covered by the grandfather provision that
had not already been issued by the effective date of the first stay
could not be issued relying upon the 1997 PM10 Surrogate
Policy as the basis for approval during the time periods that the stays
remained in effect.\6\ Prior to the stays, the grandfather provisions
remained in effect from July 15, 2008, until June 1, 2009, during which
time PSD permit applications relying on the 1997 PM10
Surrogate Policy to satisfy the PSD requirements for PM2.5
continued to be acceptable for purposes of approving and issuing the
PSD permits.
---------------------------------------------------------------------------
\6\ At the time the grandfather provision for PM2.5
was put into effect, we estimate that fewer than thirty proposed new
or modified major stationary sources were covered. Of these, at
least two projects subsequently received final and effective PSD
permits after the July 15, 2008, effective date of the final rule
and before the June 1, 2009, administrative stay took effect.
---------------------------------------------------------------------------
B. Why did EPA propose to repeal the grandfather provision for PM2.5?
On July 15, 2008, Earthjustice, acting on behalf of the Natural
Resources Defense Council and the Sierra Club, submitted a petition to
the Administrator seeking reconsideration of four provisions of the
2008 PM2.5 NSR Implementation Rule.\7\ One of the four
challenged provisions was the grandfather provision for
PM2.5 under the Federal PSD program. In the petition, the
petitioners argued that ``EPA unlawfully failed to present this
grandfather provision and accompanying rationale to the public for
comment.'' See July 15 Petition at 6. Thus, petitioners argued, EPA had
not given interested parties any notice of and the opportunity to
comment on the grandfather provision that EPA adopted in 40 CFR
52.21(i)(1)(xi) in the final rule. Moreover, with regard to the
grandfather provision itself, the petitioners questioned EPA's
authority to waive statutory requirements by establishing such a
provision, and argued that Congress specifically addressed the issue of
grandfathering in section 168(b), where it allowed for the
grandfathering of only those sources on which construction had
commenced before enactment of the 1977 Clean Air Act Amendments. See
July 15 Petition at 7.
---------------------------------------------------------------------------
\7\ Available in the docket for this rulemaking at https://www.regulations.gov, document number EPA-HQ-OAR-2003-0062-0279.1.
---------------------------------------------------------------------------
Finally, petitioners argued that the technical difficulties
associated with ambient monitoring, estimating emissions, and air
quality modeling that led to the adoption of the 1997 PM10
Surrogate Policy no longer existed. Hence, the petitioners argued that
all sources must conduct the required analyses for PM2.5
directly without relying on the 1997 PM10 Surrogate Policy,
and, therefore, there was no justification for continuing to allow any
sources to rely on the grandfather provision. See July 15 Petition at
8. In sum, petitioners asserted that the grandfather provision in 40
CFR 52.21(i)(1)(xi) was illegal and arbitrary, and requested that EPA
stay the provision.
On January 14, 2009, EPA responded in a letter to the petitioners
that the Agency was denying all aspects of the petition for
reconsideration. However, on February 10, 2009, the same petitioners
submitted a second petition similar to thefirst to EPA.\8\
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\8\ Available in the docket for this rulemaking at https://www.regulations.gov, document number EPA-HQ-OAR-2003-0062-0281.
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The second petition made the same arguments that were presented in
the July 15, 2008, petition seeking reconsideration and an
administrative stay and sought reconsideration of both the 2008
PM2.5 NSR Implementation Rule and the January 2009 denial of
petitioners' first petition for reconsideration. In response to the
second petition, the Administrator reversed the Agency's earlier
decision and agreed to reconsider each of the four challenged
provisions.
In a letter dated April 24, 2009, the Administrator indicated that
the Agency would reconsider the grandfather provision and propose to
repeal the grandfather provision ``on the grounds that it was adopted
without prior public notice and is no longer substantially justified in
light of the resolution of the technical issues with respect to
PM2.5 monitoring, emissions estimation, and air quality
modeling that led to the PM10 Surrogate Policy in 1997.''
Finally, the
[[Page 28651]]
Administrator's letter announced an administrative stay of the
grandfather provision for 3 months under the authority of section
307(d)(7)(B) of the Act.
The 3-month administrative stay became effective on June 1, 2009--
the date the notice announcing the stay was published in the Federal
Register--and ended on September 1, 2009. See 74 FR 26098. In order to
allow additional time necessary to finalize this rulemaking, EPA
proposed and promulgated a second stay that stayed the grandfather
provision until June 22, 2010. See 74 FR 48153, September 22, 2009.
During the second stay, on February 11, 2010, EPA issued a notice of
proposed rulemaking that proposed repealing the grandfather provision.
See 75 FR 6827. The same notice also proposed to end early the use of
the 1997 PM10 Surrogate Policy in PSD programs implemented
by states under an approved SIP. EPA is taking no final action on the
latter proposed action, as described further in section V of this
preamble.
C. Summary of Comments and Responses on the Proposed Repeal of the
Grandfather Provision
A total of 38 commenters, including 7 commenters speaking at the
public hearing held on February 26, 2010, responded to the 2010 notice
of proposed rulemaking. Most of these commenters specifically addressed
the proposed repeal of the grandfather provision for PM2.5
in the Federal PSD rule at 40 CFR 52.21(i)(1)(xi).
Seven commenters support the proposal to repeal the grandfather
provision, while 20 expressly opposed it. The commenters provided
various reasons for their positions. The following discussion
summarizes the significant comments and our responses categorized by
specific topics. A more detailed summary of the comments and our
responses is contained in the Response to Comment document in the
docket for this rulemaking.
1. Comments on Legal Concerns
Comments on Legality of the Grandfather Provision:
Some environmental group commenters support EPA's proposed repeal,
in part, because of their interpretation that the grandfather provision
is illegal. The commenters claim that EPA has no discretion to waive or
grandfather any permits under the Federal PSD program. On the other
hand, 12 commenters disagree that there is anything unlawful about the
grandfather provision for PM2.5. Those commenters claim that
EPA clearly has the authority to establish a grandfather provision as
part of a transition procedure for implementing new requirements. Some
of these commenters point out that EPA indicated in the 2008
PM2.5 NSR Implementation Rule that the grandfather provision
was consistent with existing grandfather provisions contained in 40 CFR
52.21(i)(1)(x).
Response:
We disagree with the comments stating that EPA may not establish
grandfather provisions in appropriate circumstances. Our decision to
repeal the grandfather provision here does not reflect any conclusion
by EPA that the grandfather provision for PM2.5, or
grandfather provisions in general, are unlawful. See also our response
to the following comments on statutory authority.
Comments on Statutory Authority:
Several commenters argue against the petitioners' claim in the 2009
petition for reconsideration that section 168(b) of the Act restricts
EPA's ability to grandfather sources by allowing for the grandfathering
of only those sources on which ``construction was commenced * * * after
June 1, 1975, and prior to the enactment of the Clean Air Act
Amendments of 1977 * * *.'' These commenters argue that Congress'
inclusion of a one-time grandfather provision upon enactment of the PSD
program is clearly different from grandfathering when a new pollutant
is identified for regulation by a NAAQS, which the Act does not
address. These commenters urge EPA to confirm that the grandfather
provision in section 168 (intended to ease transition upon enactment of
the PSD statute) does not constrain the Agency with respect to offering
reasonable transition provisions when pollutants become newly subject
to a NAAQS. The commenters argue instead that the existence of the
grandfather provision in section 168 generally indicates that Congress
intended for smooth transitions to new programs under the Act.
One of these commenters argues that in the PSD program, EPA has
included grandfather provisions when it adopted a number of new
permitting requirements, and that the Act gives EPA substantial
discretion to decide on the specifics of PSD applicability. (Citing
Envt'l Defense v. Duke Energy Corp., 127 S. Ct. 1423, 1433-34 (2007).)
Another of the commenters claims that a repeal of the grandfather
provision would be unfair and contrary to the Act.
Finally, some commenters expressly call upon EPA to clarify that it
retains the authority to issue transition policies, such as the
grandfather provision, when new NAAQS are issued.
Response:
We do not agree with the petitioners' original claim that EPA lacks
authority to adopt and implement the grandfather provision for
PM2.5. Thus, we agree with the commenters who also question
the petitioners' claim. In particular, we do not agree that the
existence of certain grandfathering in section 168(b) of the Act is
properly read to prohibit grandfathering in all other circumstances. As
discussed previously in section IV.A of this preamble, and as pointed
out in some of the comments, we have relied on the use of grandfather
provisions in past NSR regulations where we believed that it was
appropriate as part of the transition process for implementing new
requirements. In the preamble to the 2008 PM2.5 NSR
Implementation Rule, we stated our position that the PM2.5
grandfather provision is consistent with the existing provision under
40 CFR 52.21(i)(1)(x) whereby EPA grandfathered new and modified major
stationary sources with permit applications based on PM (measured as
TSP) from the then-new PM10 requirements established in
1987. However, while we continue to believe that we have the discretion
to use grandfather provisions in the PSD program where appropriate, we
have decided to repeal the grandfather provision for PM2.5
at 40 CFR 52.21(i)(1)(xi) on policy grounds, as discussed later in this
preamble.
Comments on the Section 165(c) Requirement To Issue a PSD Permit
within 1 Year:
One commenter points to section 165(c) of the Act as creating a 1-
year deadline for issuing a PSD permit after a complete application has
been submitted, and argues that since most, if not all, of the permit
applications that would be affected by the repeal of the grandfather
provision were likely submitted more than 1 year before the initial
(administrative) stay of the grandfather provision took effect, those
applications are entitled to final action consistent with the
grandfather provision and the use of PM10 as a surrogate for
PM2.5. The commenter further argues that, in addition to
allowing EPA or states with delegated PSD authority to continue ongoing
violations of the section 165(c) deadline, repealing the grandfather
provision for PM2.5 would deepen and perpetuate the
``unlawful'' effects of the stay.
Response:
We do not dispute that some of the permit applications relying on
the grandfather provision were not granted or denied within the 1-year
period provided in section 165(c) of the Act,
[[Page 28652]]
but disagree that this is a valid justification for allowing the use of
the grandfather provision, for all of the reasons discussed in this
preamble. In making this comment, the commenter has not shown that the
failure to act on those applications within 1 year can be attributed to
the stays of the grandfather provision (which, as the commenter
recognizes, came into effect almost 1 year after the grandfather
provision for PM2.5 was promulgated). Indeed, the fact that
a permit was not issued within a year during the time that the
grandfather provision was in effect suggests that there were other
factors that prevented the source from receiving a permit within the 1-
year period provided by CAA section 165(c). Moreover, even if the
grandfather provision had not been stayed with respect to those pending
applications (or if the 1997 PM10 Surrogate Policy were to
become available to the applicant through some other mechanism in the
future), it is not clear that the applications provided the information
or analyses necessary under the case law to demonstrate that
PM10 is a reasonable surrogate such that the 1997
PM10 Surrogate Policy could be used. See, e.g., discussion
of case law in 75 FR 6827, 6831-32 (February 11, 2010). Finally, if the
applicant believes that it can demonstrate that surrogacy is consistent
with the case law, then it may do so under the case law even in the
absence of EPA's 1997 PM10 Surrogate Policy.
Comments on the Legality of Repealing the Grandfather Provision for
PM2.5:
Some commenters opposing the proposed repeal of the grandfather
provision for PM2.5 argue that the repeal, in addition to
the second petition for reconsideration, is illegal. With regard to the
repeal action, some commenters question EPA's alleged position that it
must repeal the grandfather provision because there was not adequate
notice to the public of EPA's intent to continue the use of the 1997
PM10 Surrogate Policy. The commenters disagree with this
position, claiming that a failure to provide for notice and comment on
a provision of a rule cannot be a reason to repeal that provision.
One commenter disputes that there was inadequate notice because
technical difficulties of measuring, modeling, and monitoring
PM2.5 have been well known since 1997 and were fully
documented during the rulemaking. Thus, the commenter asserts that EPA
lacked the technical basis to require sources that had complete
applications pending at that time of the promulgation of the 2008
PM2.5 NSR Implementation Rule to measure or predict
PM2.5 concentration. In addition, this commenter asserts
that EPA failed to meet the administrative requirements for terminating
the 1997 PM10 Surrogate Policy. Specifically, the commenter
states that EPA would have had to provide notice of the withdrawal of
the 1997 PM10 Surrogate Policy to reverse its use by sources
grandfathered by the final 2008 PM2.5 NSR Implementation
Rule.\9\ Based on these assertions, the commenter contends that EPA may
not repeal the grandfather provision retroactively.
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\9\ In support of this position, the commenter cites Appalachian
Power v. EPA, 208 F.3d 1015, 1028 (D.C. Cir. 2001); Alaska
Professional Hunters Association v. FAA, 177 F.3d 1030, 1033-34
(D.C. Cir. 1999); and Paralyzed Veterans of America v. D.C. Arena
L.P., 117 F.3d 579, 586 (D.C. Cir. 1997).
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Two commenters believe that the grandfather provision, while not
explicitly proposed, was a logical outgrowth of the proposal. One of
the commenters expresses the belief that EPA raised for comment, in the
2005 PM2.5 Implementation Rule proposal, issues concerning
appropriate means for and timing of the transition to implementation of
PM2.5 requirements in the PSD program. The other commenter
alleges that the 2005 PM2.5 Implementation Rule proposal
expressly announced continued use of the 1997 PM10 Surrogate
Policy as Option 1 at 70 FR 66044 and solicited comment on this
approach.
The latter commenter also argues that the 2010 proposal to repeal
the grandfather provision for PM2.5 represents a dangerous
procedural precedent. While acknowledging that some actions adopted in
a final rule could clearly be outside the scope of the proposed rule,
the commenter asserts that as an overarching rule, the determination of
whether regulatory actions adopted by a previous Administration's final
rule were a logical outgrowth of the proposed rule should be left for
the courts to decide. The commenter believes that leaving such
decisions to the courts will ensure objective and consistent
determinations of administrative law, rather than politically-
influenced determinations that likely will shift from Administration to
Administration. The commenter contends that the grandfather provision
is not an instance that warrants EPA's departure from that principle.
One commenter claims that the issue of the lawfulness of the
grandfather provision was previously addressed and decided by EPA in
the January 14, 2009, denial of the first petition for reconsideration
of the final 2008 PM2.5 NSR Implementation Rule. The
commenter contends that EPA's reliance on the second petition for
reconsideration, filed on February 10, 2009, is contrary to section
307(d)(7)(B) of the Act because the second petition did not contain any
new information that would justify reconsideration and, thus, the
second petition was untimely and unfounded.
Response:
We do not agree with the commenters' claim that we are repealing
the grandfather provision because of the lack of adequate notice to the
public. The lack of prior public notice was a basis only for granting
reconsideration and going through a subsequent rulemaking. EPA's
decision to repeal the grandfather provision is not based on the fact
that the provision was not explicitly proposed in the 2005
PM2.5 Implementation Rule proposal. EPA in this rule is not
taking any position on whether a lack of public notice could be a basis
for repealing a rule, or on the other issues that these comments raise
concerning the adequacy of public notice, logical outgrowth, the
timeliness of the second petition for reconsideration, and other
procedural matters.
We believe that the Act provides EPA with sufficient authority to
issue transition policy, including grandfather provisions, as needed to
provide for the reasonable implementation of new NSR requirements. This
is evidenced by the fact that we have established grandfather
provisions in the past, as described in section IV.A of this preamble.
However, it should not be taken to mean that we have or intend to
automatically use grandfathering as a transition mechanism for all
changes in NSR requirements. In this case, we continue to believe that
the technical tools needed to carry out a PM2.5 analysis are
currently available to the degree necessary to justify requiring
sources to comply with the PM2.5 requirements via
PM2.5 analyses for BACT and air quality impacts. Indeed,
this is what all other sources that are not subject to the grandfather
provision but are located in areas subject to the Federal PSD program
are required to do. Alternatively, sources may use an appropriate
surrogacy demonstration in accordance with past court decisions. For
this reason and the other substantive reasons discussed in this
preamble, we have decided to repeal the grandfather provision for
PM2.5.
Finally, we wish to clarify a point made by the commenter who
alleged that the 2005 PM2.5 Implementation Rule proposal
expressly announced and sought comment on the continued use of the 1997
PM10 Surrogate Policy as Option 1. That proposal actually
[[Page 28653]]
proposed to allow the continued use of the 1997 PM10
Surrogate Policy only for states that have SIP-approved PSD programs
and need additional time to revise their rules to address the
PM2.5 requirements. For all other circumstances involving
the NSR rules, we clearly stated that PSD applicants would be subject
to the PM2.5 requirements as of the effective date of the
final rule. See 70 FR 66043-44.
2. Comments on the Burden on Sources Resulting From Repeal of the
Grandfather Provision
In the 2010 proposal to repeal the grandfather provisions for
PM2.5, EPA solicited comments on the burdens that may be
incurred by sources affected by a repeal of the grandfather provision.
See 75 FR 6833. Several commenters express concern that repeal of the
grandfather provision would unfairly penalize permit applicants who
were in the process of obtaining construction permits.
Comment:
One commenter states that repeal would effectively impose
retroactive requirements on sources that relied on past EPA statements
of the law and the effect of the Agency's regulations, which goes
against the concepts of fundamental fairness and equity.
Response:
We disagree with the premise of this comment: that the repeal of
the grandfather provision imposes new requirements. The 1997
PM10 Surrogate Policy did not eliminate any PSD
requirements; it simply provided an alternative means of demonstrating
compliance with the applicable requirements that were already in the
PSD regulations at 40 CFR 52.21 when the PM2.5 NAAQS became
effective in 1997. Thus, the repeal of the grandfather provision does
not impose new requirements on any source. The commenter's concern
about the fairness of our decision is addressed in the next response.
Comment:
Some commenters indicate that repeal would result in ``permit
gridlock.'' These commenters state that each regulatory change adds
another year onto the permitting process, during which more regulations
could change and add further delay. The commenters contend that because
of the length of the process, the major applicable rules need to stay
constant (in all but extraordinary circumstances) in order for the
process to proceed in a logical and orderly fashion.
Another commenter claims that repeal of the grandfather provision
would arbitrarily and unreasonably penalize applicants for the delay of
the reviewing authority in discharging its permitting responsibilities.
The commenter provides an example where two applicants (Applicants A
and B) submit complete applications on the same date more than a year
before the effective date of the stay of the grandfather provision, but
Applicant A's permit is approved and issued before the effective date
of the stay and Applicant B's permit is not yet ready to be issued on
the effective date of the stay. The commenter concludes that, through
no fault of Applicant B, EPA's violation of its nondiscretionary
statutory duty to act within 1 year would impose on the applicant the
significant costs and delay involved in undertaking a new analysis of
PM and, potentially, revising the permit application.
One commenter opines that an important principle underlies all
grandfather provisions, including this PM2.5 grandfather
provision. This principle is that a source that relies in good faith on
EPA's existing standards and procedures to design a construction
project and prepare a PSD permit application based upon that design
should have the right to rely upon those existing standards and
procedures and should not later be penalized retroactively when the
standards and/or procedures change and, more importantly, go into
effect after the application was submitted.
The same commenter goes on to point out that the issuance of a PSD
permit under the grandfather provision would not establish any future
waiver of compliance or long-term exemption under law or in practice
because the Act requires all sources, including those that have
undergone PSD review, to comply with limitations the state determines
in its SIP are necessary to meet NAAQS (including any future revised
NAAQS) as well as to comply with any New Source Performance Standards.
According to the commenter, this ensures that, regardless of whether a
source avoided direct evaluation of its PM2.5 emissions
during NSR because of the grandfather provision, its PM2.5
emissions will still be evaluated for compliance with the
PM2.5 NAAQS.
Response:
In projecting the burdens of extended permitting time and effort,
the commenters assume that if we did not repeal the grandfather
provision, sources could rely on the 1997 PM10 Surrogate
Policy without further analysis. However, as discussed in the 2010
proposal preamble (see 75 FR 6831-32) and later in section V.C.1.b of
this preamble, at present sources are only able to use the policy after
completing a surrogacy demonstration consistent with the case law
(i.e., PM10 must be shown to be a reasonable surrogate for
PM2.5 under the circumstances of the specific permit) and
within the limits of the policy itself (i.e., there must be continuing
technical reasons why a PM2.5 analysis is not technically
feasible). These key prerequisites cannot be assumed to be met
automatically, and the commenters have not shown these prerequisites to
be met with respect to any of the applications that would be covered by
the grandfather provision. Thus, even if the grandfather provision were
to remain in force, additional analysis would be required of sources
seeking to continue using the 1997 PM10 Surrogate Policy
under that provision.
The EPA has considered the comments concerning how a repeal of the
grandfather provision might impact the permitting process and allegedly
create unfairness and inequity in some of the hypothetical
circumstances described in the comments. We recognize that the
commenters' concerns pertain to the fairness of our proposal to change
the procedures for demonstrating compliance with the PM2.5
requirements in mid-permit process for individual permits. However, we
believe that we have an obligation to weigh those concerns and
associated burdens against our interpretation of the Act, which
requires that PSD sources must demonstrate that their emissions will
not cause or contribute to a violation of the PM2.5 NAAQS,
and such demonstration should provide adequate assurance that such
compliance will occur. We believe that the 1997 PM10
Surrogate Policy, which has been in effect for about 13 years, no
longer provides an acceptable means of making the required
demonstration in light of the availability of the technical tools
needed to complete a PM2.5 analysis. Thus, as part of our
obligation to evaluate the need for transition policy both initially
and on an ongoing basis, we have concluded that such burdens are
neither unfair nor inequitable in comparison to the benefits associated
with having a better understanding of the impacts the source's
emissions will have on the PM2.5 NAAQS. This conclusion is
based on our belief that the approach set forth in the 1997 EPA policy
memo, while necessary in the absence of the technical tools needed to
implement the PSD program for PM2.5 directly, is
sufficiently deficient in its ability to satisfy the PM2.5
requirements (in that it lacks a surrogacy demonstration), particularly
with regard to possible
[[Page 28654]]
adverse impacts on the PM2.5 NAAQS, that it should no longer
be available as a means of meeting those requirements now that the
necessary technical tools for a PM2.5 analysis are
available. Case law allows the use of surrogates when properly applied.
Hence, we point out that the use of a valid surrogate approach in
general is not prohibited by our action in this final rule.
Finally, we note that we did not stay the grandfather provision
until almost 1 year following its effective date. Some permits were
issued during the time that the grandfather provision was in effect.
Grandfathered sources for which a PSD permit was not issued during that
period likely had problems related to factors other than the
PM2.5 analyses that prevented the source from receiving a
permit.
3. Comments on the Number of Sources Affected by Repeal
Comment:
We did not receive any comments that either validate or dispute the
number of sources that we estimated would be affected by the stay of
the grandfather provision for PM2.5.\10\ One commenter
observes that EPA has recognized that continued use of the grandfather
provision would affect very few, if any, still-pending permits, and
finds it hard to understand why EPA feels it necessary not only to
discontinue the grandfather provision altogether, but also to do so
immediately by issuing the administrative stay. This commenter believes
that the facts presented by EPA undercut the petitioners' claim that
grandfathering certain permit applications presents an irreparable
harm.
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\10\ A state agency commenter claims that EPA's repeal of the
grandfather provision for PM2.5 could affect up to 16 of
the agency's pending PSD projects. However, this agency's PSD
program is part of an EPA-approved SIP and, as such, does not appear
to be affected by the grandfather provision. Instead, we believe
that the affected PSD projects would be affected by the ending of
the 1997 PM10 Surrogate Policy. Thus, we address this
comment in the section V, where our final action on ending the 1997
PM10 Surrogate Policy in SIP-approved PSD programs is
addressed.
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Response:
In the 2010 proposal to repeal the grandfather provision, we
reported that we were aware of 27 sources that had submitted PSD permit
applications under the Federal PSD program prior to July 15, 2008-- the
effective date of the 2008 PM2.5 NSR Implementation Rule--
but did not receive their permits by that date. Thus, these
applications fell within the scope of the grandfather provision at the
time it was promulgated. For at least six of these applications, the
permit was either issued or denied, or the project was cancelled, prior
to June 1, 2009, when the administrative stay became effective. For
most of the remaining 21 applications, it is our understanding that the
sources have already directly addressed, or are planning to directly
address, the applicable PM2.5 requirements in order to
obtain a permit. At least two of the sources are reportedly planning to
take enforceable emissions limitations on their PM2.5
emissions in order to avoid the PSD requirements for PM2.5
altogether.
Although only a few remaining grandfathered sources would be
affected by a repeal of the grandfather provision, we believe that any
air quality assessment contained in a PSD permit should reflect as
accurately as possible the actual impacts that could be experienced in
the area of concern. We do not believe that an analysis of
PM10 emissions impacts on the PM10 NAAQS
sufficiently represents the potential impacts that a source may have on
the PM2.5 NAAQS. We did not base our decision to repeal the
grandfather provision on the number of sources that could ultimately
have to submit revised analyses to satisfy the PSD requirements for
PM2.5.
4. Comments on Retroactive Implementation
Comment:
Several commenters who opp