Operating Permit Programs and Prevention of Significant Deterioration (PSD) and Nonattainment New Source Review (NSR); Flexible Air Permitting Rule, 52206-52261 [E7-17418]
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Federal Register / Vol. 72, No. 176 / Wednesday, September 12, 2007 / Proposed Rules
40 CFR Parts 51, 52, 70, and 71
[EPA–HQ–OAR–2004–0087, FRL–8462–9]
RIN 2060–AM45
Operating Permit Programs and
Prevention of Significant Deterioration
(PSD) and Nonattainment New Source
Review (NSR); Flexible Air Permitting
Rule
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
jlentini on PROD1PC65 with PROPOSALS2
AGENCY:
SUMMARY: We are proposing to revise the
regulations governing State and Federal
operating permit programs required by
title V of the Clean Air Act (CAA or the
Act) and the New Source Review (NSR)
programs required by parts C and D of
title I of the Act. These proposed actions
are based, in large part, on the lessons
learned through EPA’s pilot experience
in which EPA worked closely with
States and certain sources subject to title
V permitting requirements to develop
flexible air permitting approaches that
provide greater operational flexibility
and, at the same time, ensure
environmental protection and
compliance with applicable laws.
In pilot permits, increased flexibility
is primarily achieved through advance
approvals under NSR and alternative
operating scenarios (AOSs). The
proposed revisions clarify how this can
often be done in the existing regulatory
framework of the operating permit
programs. The proposed revisions also
add major NSR requirements for Green
Groups, which allow future changes to
occur within a group of emissions
activities, provided that they are ducted
to a common air pollution control
device which is determined to meet
‘‘best available control technology’’
(BACT) or ‘‘lowest achievable emission
rate’’ (LAER), as applicable and that
they are determined to comply with all
relevant ambient requirements.
DATES: Comments. Written comments
must be received on or before November
13, 2007. Under the Paperwork
Reduction Act, comments on the
information collection provisions must
be received by OMB on or before
October 12, 2007.
Public Hearing. If anyone contacts
EPA requesting to speak at a public
hearing by October 2, 2007, we will
hold a public hearing approximately 30
days after publication in the Federal
Register. Additional information about
the hearing would be published in a
subsequent Federal Register notice.
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Comments. Submit your
comments, identified by Docket ID No.
EPA–HQ–OAR–2004–0087, by one of
the following methods:
• https://www.regulations.gov: Follow
the on-line instructions for submitting
comments.
• E-mail: a-and-r-Docket@epa.gov.
• Fax: (202) 566–9744.
• Mail: Environmental Protection
Agency, EPA Docket Center (EPA/DC),
Air and Radiation Docket, Mail Code
2822T, 1200 Pennsylvania Avenue,
NW., Washington, DC 20460. Please
include two copies. In addition, please
mail a copy of your comments on the
information collection provisions to the
Office of Management and Budget
(OMB), Attn: Desk Officer for EPA, 725
17th St., NW., Washington, DC 20503.
• Hand Delivery: EPA Docket Center,
(Air Docket), U.S. Environmental
Protection Agency, Room 3334, 1301
Constitution Ave., NW., Washington,
DC. Such deliveries are only accepted
during the Docket’s normal hours of
operation, and special arrangements
should be made for deliveries of boxed
information.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–OAR–2004–
0087. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through www.regulations.gov
or e-mail. The www.regulations.gov Web
site is an ‘‘anonymous access’’ system,
which means EPA will not know your
identity or contact information unless
you provide it in the body of your
comment. If you send an e-mail
comment directly to EPA without going
through www.regulations.gov, your email address will be automatically
captured and included as part of the
comment that is placed in the public
docket and made available on the
Internet. If you submit an electronic
comment, EPA recommends that you
include your name and other contact
information in the body of your
comment and with any disk or CD–ROM
you submit. 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. Electronic files should avoid
the use of special characters, any form
of encryption, and be free of any defects
or viruses. For additional instructions
ADDRESSES:
ENVIRONMENTAL PROTECTION
AGENCY
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on submitting comments, go to I C & D
of the SUPPLEMENTARY INFORMATION
section of this document.
Docket: All documents in the docket
are listed in the index at
www.regulations.gov. Although listed in
the index, some information is not
publicly available, i.e., CBI or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
is not placed on the Internet and will be
publicly available only in hard copy
form. Publicly available docket
materials are available either
electronically in www.regulations.gov or
in hard copy at the EPA Docket Center
(Air Docket), EPA West, Room 3334,
1301 Constitution Ave., NW.,
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: For
issues concerning advance approvals
and AOSs, contact Michael Trutna, Air
Quality Policy Division (C504–01), U.S.
Environmental Protection Agency,
Research Triangle Park, NC 27711;
telephone (919) 541–5345, fax number
(919) 541–4028; or electronic mail at
trutna.mike@epa.gov.
For issues concerning ARMs and
EPA’s pilot permits, contact David Beck,
Office of Policy, Economics, and
Innovation, Innovative Pilots Division
(C304–05), U.S. Environmental
Protection Agency, Research Triangle
Park, NC 27711; telephone (919) 541–
5421, fax number (919) 541–2664; or
electronic mail at beck.david@epa.gov.
For issues relating to monitoring,
recordkeeping, and reporting for flexible
air permits, contact Barrett Parker,
Sector Policies and Programs Division,
Measurement Policy Group (D243–03),
U.S. Environmental Protection Agency,
Research Triangle Park, NC 27711;
telephone 919–541–5635, fax number
(919) 541–1039; or electronic mail at
parker.barrett@epa.gov.
For other part 70 issues, contact Juan
Santiago, Operating Permits Group, Air
Quality Policy Division (C504–05), U.S.
Environmental Protection Agency,
Research Triangle Park, NC 27711;
telephone (919) 541–1084, fax number
(919) 541–5509; or electronic mail at
santiago.juan@epa.gov.
For issues relating to Green Groups,
contact Dave Painter, New Source
Review Group, Air Quality Policy
Division (C504–03), U.S. Environmental
Protection Agency, Research Triangle
Park, NC 27711; telephone (919) 541–
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5515, fax number (919) 541–5509; or
electronic mail at
painter.david@epa.gov.
To request a hearing or information
pertaining to a hearing on this
document, please contact Pam Long, Air
Quality Policy Division, U.S. EPA,
Office of Air Quality Planning and
Standards (C504–03), Research Triangle
Park, North Carolina 27711, telephone
number (919) 541–0641, facsimile
number (919) 541–5509; electronic mail
e-mail address: long.pam@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. What are the regulated entities?
Entities potentially affected by these
proposed actions are facilities currently
required to obtain title V permits under
State, local, tribal, or Federal operating
permits programs, and State, local, and
tribal governments that are authorized
by EPA to issue such operating permits.
Other entities potentially affected by
this proposed action are facilities
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required to obtain major NSR permits
under State, local, tribal, or Federal
major NSR programs, and State, local,
and tribal governments that issue such
permits pursuant to approved part 51
major NSR programs. Potentially
affected sources are found in a wide
variety of industry groups. In particular,
we believe based on our experience in
implementing our flexible air permit
pilot program that these groups will
include, but are not limited to, the
following:
Industry group
SIC a
NAICS b
Aerospace Manufacturing ...............
Automobile Manufacturing ..............
372 .................................................
371 .................................................
Industrial Organic Chemicals ..........
Chemical Processes .......................
Converted Paper and Paperboard
Products.
Magnetic Tape Manufacturing ........
Petroleum Refining ..........................
Other Coating Operations ...............
286 .................................................
281 .................................................
267 .................................................
Paper Mills ......................................
Pharmaceutical Manufacturing ........
Printing and Publishing ...................
Pulp and Paper Mills .......................
Semi-conductors .............................
Specialty Chemical Batch Processes.
262 .................................................
283 .................................................
275 .................................................
262 .................................................
367 .................................................
282, 283, 284, 285, 286, 287, 289,
386.
336411, 336412, 332912, 336411, 335413.
336111, 336112, 336712, 336211, 336992, 336322, 336312, 33633,
33634, 33635, 336399, 336212, 336213.
325191, 32511, 325132, 325192, 225188, 325193, 32512, 325199.
325181, 325182, 325188, 32512, 325131, 325998, 331311.
322221, 322222, 322223, 322224, 322226, 322231, 326111, 326112,
322299, 322291, 322232, 322233, 322211.
334613.
32411.
313311, 313312, 314992, 33132, 337122, 337121, 337124, 337215,
337129, 37125, 337211, 337214, 337127, 322221, 322222,
322226, 335221, 335222, 335224, 335228, 333312, 333415,
333319.
322121, 322122.
325411, 325412, 325413, 325414.
323114, 323110, 323111, 323113, 323112, 323115, 323119.
32211, 322121, 322122, 32213.
334413.
3251, 3252, 3253, 3254, 3255, 3256, 3259, except 325131 and
325181.
369 .................................................
291 .................................................
226, 229, 251, 252, 253, 254, 267,
358, 363.
a Standard
b North
Industrial Classification
American Industry Classification System.
B. What should I consider as I prepare
my comments for EPA?
1. Submitting CBI
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Do not submit this information to EPA
through www.regulations.gov or e-mail.
Clearly mark the part or all of the
information that you claim to be CBI.
For CBI information in a disk or CD–
ROM that you mail to EPA, mark the
outside of the disk or CD–ROM as CBI
and then identify electronically within
the disk or CD–ROM the specific
information that is claimed as CBI. In
addition to one complete version of the
comment that includes information
claimed as CBI, a copy of the comment
that does not contain the information
claimed as CBI must be submitted for
inclusion in the public docket.
Information so marked will not be
disclosed except in accordance with
procedures set forth in 40 CFR part 2.
2. Suggestions for Preparing Your
Comments
When submitting comments,
remember to:
• Identify the rulemaking by docket
number and other identifying
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information (subject heading, Federal
Register date and page number).
• Follow directions. The Agency may
ask you to respond to specific questions
or organize comments by referencing a
Code of Federal Regulations (CFR) part
or section number.
• Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
• Describe any assumptions and
provide any technical information and/
or data that you used.
• If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
• Provide specific examples to
illustrate your concerns, and suggest
alternatives.
• Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
• Make sure to submit your
comments by the comment period
deadline identified.
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C. 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
proposal will also be available on the
WWW. Following signature by the EPA
Administrator, a copy of this notice will
be posted in the regulations and
standards section of our NSR home page
located at https://www.epa.gov/nsr.
D. How Can I Find Information About a
Possible Hearing?
Persons interested in presenting oral
testimony should contact Pam Long, Air
Quality Policy Division (C504–03), U.S.
EPA, Research Triangle Park, NC 27711,
telephone number (919) 541–0641 or email long.pam@epa.gov at least 2 days
in advance of the public hearing.
Persons interested in attending the
public hearing should also contact Pam
Long to verify the time, date, and
location of the hearing. The public
hearing will provide interested parties
the opportunity to present data, views,
or arguments concerning these proposed
rules.
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E. How is this preamble organized?
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The information presented in this
preamble is organized as follows:
I. General Information
A. What are the regulated entities?
B. What should I consider as I prepare my
comments for EPA?
C. Where can I get a copy of this document
and other related information?
D. How can I find information about a
possible hearing?
E. How is this preamble organized?
II. What is a flexible air permit and the
background related to this action?
A. What is a flexible air permit?
B. What is the statutory background?
C. What is the regulatory background
relating to the proposed revisions to
parts 70 and 71?
D. What is the regulatory background
relating to the proposed revisions to
parts 51 and 52?
III. What is the purpose of this action?
IV. What experience did we gain from our 12year pilot permit experience?
A. What were the benefits of the pilot
permits?
B. What were the conclusions of the
sources, permitting authorities, and EPA
about flexible permits?
C. What are EPA’s recommendations for
public participation in flexible
permitting?
V. What are the key elements of this
proposal?
A. What are the key elements of proposed
revisions to parts 70 and 71?
B. What are the key elements of proposed
revisions to parts 51 and 52?
VI. What changes are we are proposing to
parts 70 and 71?
A. What is our proposed definition of an
AOS, and how does it provide a source
operational flexibility?
B. What information is necessary in a title
V permit application to seek approval of
an AOS?
C. What terms and conditions must be
included in the title V permit for
approved AOSs?
D. What are some examples of how AOSs
and advance approvals can be used to
provide operational flexibility?
E. What is the process for adding or
revising advance approvals, AOSs, and
ARMs in issued permits?
F. How do the proposed AOS provisions
differ between parts 70 and 71?
VII. What changes are we proposing in parts
51 and 52?
A. What are the benefits of Green Groups?
B. What is a Green Group?
C. How is a Green Group designation
incorporated into a title V permit?
D. What is the legal rationale for Green
Groups?
E. What are the conforming regulatory
changes we must make to implement the
Green Group concept?
F. What is an example of how a Green
Group might be used in combination
with a title V permit?
VIII. What is the effect of these proposed
revisions?
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A. If these proposed revisions are finalized,
what are the implications for approved
part 70 programs?
B. What are the implications for NSR
programs?
IX. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act (RFA)
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
II. What is a flexible air permit and the
background related to this action?
In this section, we first explain what
is a flexible air permit. We then provide
an overview of the relevant statutory
provisions and describe the regulatory
and other actions taken over the course
of the last decade that are relevant to
this proposal.
A. What is a flexible air permit?
A flexible air permit is a title V permit
that facilitates flexible, marketresponsive operations at a source
through the use of one or more
permitting approaches, while ensuring
equal or greater environmental
protection as achieved by conventional
permits.1 In particular, flexible
permitting approaches allow the source,
under protection of the permit shield, to
make certain types of physical and
operational changes without further
review or approval by the permitting
authority. One approach includes, for
example, obtaining advance approval
for anticipated changes (such as through
a minor NSR action), incorporating the
advance approval into the title V permit,
and adding terms in the title V permit
as necessary to assure compliance with
all other applicable requirements
implicated by the anticipated changes.
Another approach is to establish one or
more alternative operating scenarios
(AOSs) in a title V permit to allow
existing emissions units the flexibility
to operate in varying ways and/or at
varying rates of production, where such
variations would be subject to different
applicable requirements but would not
require prior authorization (i.e., advance
approval).
1 We first addressed the concept of a flexibile air
permit in May 1991. See 56 FR 21712, 21748 (May
10, 1991).
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For more than a decade, we
participated in a pilot flexible air
permitting program with certain title V
sources and permitting authorities
through which we tested and evaluated
various permitting approaches that
afford operational flexibility. The
lessons learned through the pilot
program, in part, served as the basis for
our adoption of the plantwide
applicability limitation (PAL)
provisions of the 2002 NSR
Improvement rule. They also serve as a
basis for this rule, where we seek to
build upon existing regulatory
provisions that afford operational
flexibility. We believe that the flexible
permitting approaches in this proposed
rulemaking provide a path forward for
sources to more effectively and
proactively manage their title V and
NSR permitting obligations, while
ensuring environmental protection.
B. What is the statutory background?
There are two aspects of the CAA that
are relevant to this proposed rule: title
V and parts C and D of title I of the Act.
In 1990, Congress promulgated title V
and established the operating permit
program. That program requires certain
stationary sources to obtain operating
permits as a mechanism for gathering all
applicable requirements of the Act for
each affected source into one
comprehensive document.2 See H.R.
Conference Report No. 101–952,
reprinted in U.S.C.C.A.N. 3867, 3877
(1990).
One of the key purposes of the title V
operating permit program is to enable
the source, the State or local permitting
authority, EPA, and the public to gain
a better understanding of the
requirements of the Act to which the
source is subject. The ability to assess
and achieve compliance with the law is
improved by virtue of having one
comprehensive operating permit
containing all applicable requirements
for a source. The title V permit program
does not impose new substantive air
quality control requirements. It does,
however, require that fees be imposed
on sources and that certain procedural
measures be followed, especially with
respect to determining compliance with
applicable requirements. See, e.g., CAA
sections 502(b)(3), 503(b)(2), and 504(a).
2 ‘‘Applicable requirements’’ is a term that is used
in title V. The EPA has defined the term to include,
among other things, State implementation plan
(SIP) rules, the terms and conditions of
preconstruction permits issued under a SIPapproved NSR program, and requirements pursuant
to the new source performance standards (NSPS),
national emission standards for hazardous air
pollutants (NESHAP), and Acid Rain Programs. See
40 CFR 70.2.
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The Act affirms that State and local
governments have primary
responsibility for air quality. See CAA
section 101(a)(3). Title V vests primary
responsibility for issuing operating
permits with State and local
governments. See CAA section 502.
Congress required EPA to promulgate
regulations establishing the minimum
elements of a title V operating permits
program. See CAA section 502(b)
(articulating ten minimum elements for
State programs). In establishing such
minimum elements, Congress directed
that EPA develop ‘‘[a]dequate,
streamlined, and reasonable
procedures’’ for processing and
reviewing permit applications and for
the expeditious review of permit
actions. See CAA section 502(b)(6).
As explained below, EPA
promulgated regulations establishing
the minimum requirements for a State
operating permit program in 1992.
These regulations are codified at 40 CFR
part 70 and are often referenced as ‘‘part
70.’’ In addition to requiring EPA to
establish the minimum elements for the
operating permits program, Congress
required each State to develop and
submit to EPA for approval an operating
permit program that meets the
requirements of the Act and part 70. See
CAA section 502(d)(1). In areas that do
not have an approved State, local, or
tribal title V program, EPA administers
the operating permit program as a
Federal program pursuant to regulations
set out in 40 CFR part 71. See CAA
section 502(d)(3). Title V requires that
each operating permit contain terms
sufficient to assure compliance with all
applicable air requirements. See CAA
section 504(a).
The other parts of the Act relevant to
this rule include part C, entitled
‘‘Prevention of Significant Deterioration
of Air Quality’’ (typically referred to as
‘‘PSD’’), and part D, entitled ‘‘Plan
Requirements for Nonattainment Areas’’
(typically referred to as ‘‘nonattainment
major NSR’’), of title I of the Act. See
CAA sections 160 through 169B (part C)
and 171 through 193 (part D). These
parts together are commonly referred to
as the major NSR program. This
program is a preconstruction review and
permitting program applicable to new or
modified major stationary sources of air
pollutants regulated under the Act. The
implementing regulations for the
program are contained in 40 CFR
51.165, 51.166, 52.21, 52.24, and part
51, appendix S.
The PSD provisions apply to new
major sources and to major
modifications at existing major sources
for pollutants where the area in which
the source is located is in attainment or
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unclassifiable with the national ambient
air quality standards (NAAQS). A
source that is subject to PSD must
install BACT and perform an air quality
analysis and an additional impacts
analysis, and there must be an
opportunity for public participation. See
CAA section 165(a). The BACT is an
emissions limitation that is based on the
maximum degree of control that can be
achieved, as determined on a case-bycase basis for each source considering
energy, environmental, and economic
impacts. See CAA section 169(3); 40
CFR 51.166(b)(12), 52.21(b)(12), and
51.165(a)(1)(xl). The source’s air quality
analysis must demonstrate that the
source will not cause or contribute to a
violation of any NAAQS or any
maximum allowable increase in ambient
concentration either for a Class I area or
as established under the PSD program
(typically referred to as ‘‘PSD
increments’’). See CAA section
165(a)(3).
Nonattainment major NSR applies to
new major sources and to major
modifications at existing major sources
for pollutants where the area in which
the source is located is not in attainment
with the NAAQS.3 Nonattainment major
NSR requires the source to comply with
lowest achievable emission rate
(‘‘LAER’’) and to obtain sufficient
emissions offsets, and there must be an
opportunity for public involvement. See
CAA section 173(a); 40 CFR 51.161. The
LAER is determined for each source to
reflect the more stringent of the
following: (1) The most stringent
emissions limitation that is contained in
any State implementation plan (SIP) for
that type of source (if achievable for the
proposed source), or (2) the most
stringent emissions limitation that is
achieved in practice for that type of
source. See CAA section 171(3); 40 CFR
51.165(a)(1)(xiii).4
In addition to a major NSR program,
States are required to have ‘‘minor’’ NSR
programs, which apply to new and
modified sources that do not meet the
emissions thresholds for major NSR. See
section 110(a)(2)(C) of the Act. The
minor NSR program is part of a State’s
implementation plan and is designed to
ensure that the construction or
modification of an affected source does
not violate any portion of the SIP and
does not interfere with the attainment of
3 ‘‘Major stationary source’’ is defined at 40 CFR
51.165(a)(1)(iv), 51.166(b)(1), and 52.21(b)(1), and
‘‘major modification’’ is defined at 40 CFR
51.165(a)(1)(v), 51.166(b)(2), and 52.21(b)(2).
4 This is a section 307(d) rulemaking. See CAA
section 307(d)(1)(J) (addressing regulations under
part C of Subchapter I) and 307(d)(1)(V)
(authorizing the Administrator to designate any
action a 307(d) rulemaking).
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the NAAQS or cause the exceedance of
any applicable PSD increments.
C. What is the regulatory background
relating to the proposed revisions to
parts 70 and 71?
This proposed rule addresses certain
permitting mechanisms for providing
operational flexibility. The concept of
operational flexibility is not a new one.
In July 1992, under the authority of title
V of the Act, we finalized the part 70
State operating permit program
regulations.5 See 57 FR 32250 (July 21,
1992); 40 CFR part 70. Those regulations
include operational flexibility
provisions, one of which is the AOS
provision found at 40 CFR 70.6(a)(9). It
is this provision that is the primary
subject of these proposed revisions.6
This section 40 CFR 70.6(a)(9) generally
provides that any permit issued under
part 70 must include terms and
conditions for reasonably anticipated
operating scenarios approved by the
permitting authority. EPA promulgated
40 CFR 70.6(a)(9) pursuant to the
authority of section 502(b)(6) of the
CAA, which directs that operating
permit programs include ‘‘[a]dequate,
streamlined, and reasonable
procedures’’ for processing and
reviewing permit applications and for
the expeditious review of permit
actions.
In the final part 70 rule, we
emphasized the importance of 40 CFR
70.6(a)(9), noting that a permit that
contains approved AOSs ‘‘will be a
more complete representation of the
operation at the permitted facility.’’ See
57 FR 32276. We also explained that
once a flexible air permit with approved
AOSs is issued, the need for additional
permit modifications will be
substantially reduced since the permit
will already contain appropriate terms
and conditions to accommodate the
approved operating scenarios. In the
final part 70 rule, we did not place any
restrictions on the types of operations
that could qualify as a reasonably
anticipated operating scenario.7
5 In the 1990’s, we proposed certain clarifications
and modifications to the part 70 regulations, none
of which were ever finalized. See generally 60 FR
45529 (Aug. 31, 1995), 59 FR 44460 (Aug. 29, 1994).
In those proposals, among other things, we
discussed the concept of ‘‘advance NSR’’ in relation
to AOSs, and proposed a definition for ‘‘alternative
operating scenarios.’’
6 The EPA included other operational flexibility
provisions in the final part 70 regulations,
including 40 CFR 70.4(b)(12), (b)(14) and (b)(15),
which implement section 502(b)(10) of the Act.
This proposed rule does not address these
provisions.
7 The Federal operating permit program at part 71
addresses reasonably anticipated operating
scenarios in the same fashion as part 70. See 40 CFR
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Shortly after we finalized the part 70
State operating permit program, we
initiated a pilot title V permit program
with interested States, and our program
continues to the present. See section IV
of this preamble for more discussion.
Companies participating in the pilot
program sought to reduce the cost, time,
and delays associated with a permit
revision for each operational change at
a facility. We and the States sought to
increase the sources’ operational
flexibility, while assuring compliance
with applicable requirements, ensuring
environmental protection, and
facilitating P2. These pilots typically
allowed for both changes to operations
of existing emissions units and the
addition of entirely new emissions
units, provided that the changes were
sufficiently well described in the permit
application so that the permitting
authority could confirm that all
applicable requirements were identified
and that the permit contained terms and
conditions assuring compliance with all
applicable requirements.8
To evaluate the flexible pilot permits
program, we conducted a thorough
review of six of the pilot permits for
which at the time there was significant
implementation experience.9 We
reviewed on-site records to track
utilization of the flexible permit
provisions, assessed how well the
permits worked, evaluated total
emissions reductions achieved, and
analyzed the economic benefits
associated with the permits. Overall, we
found that significant environmental
benefits had occurred for each of the
permits reviewed. At the time of the
evaluation, each of the sources had
achieved 25- to 80-percent reductions in
actual plantwide emissions or emissions
71.6(a)(9). These proposed revisions affect both
parts 70 and 71 and the revisions that we propose
to each part are virtually identical. For ease of
reference, this preamble discussion refers to the
part 70 provisions. The discussion, of course,
applies equally to the part 71 program revisions
proposed. Section numbers given for the part 70
rules correspond directly to the analogous sections
in part 71. The term ‘‘title V permit’’ refers to
permits issued under either part 70 or part 71.
8 In implementing the pilot projects, EPA and
other permitting authorities sometimes imposed
certain constraints in the permits for advance
approvals and AOSs beyond those expressly
contained in applicable requirements or part 70.
These additional constraints varied and were
designed to provide permitting authorities the
opportunity to gain experience with different
flexible permitting approaches. Some of these
constraints were anticipated to be removed at the
time of permit renewal in the next version of the
permit.
9 See ‘‘Evaluation of the Implementation
Experience with Innovative Air Permits.’’ A copy of
this report is located in the docket for this
rulemaking, or can be accessed at https://
www.epa.gov/ttn/oarpg/t5/memoranda/
iap_eier.pdf.
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per unit of production. We made a
series of findings based on our
evaluation of the permits. See
‘‘Evaluation of the Implementation
Experience with Innovative Air
Permits’’ and section IV of this
preamble, which summarizes the
findings of this study.10
D. What is the regulatory background
relating to the proposed revisions to
parts 51 and 52?
Based on our pilot permit evaluation
and our 1996 proposed modifications to
the major NSR program, in December
2002, we finalized the NSR
Improvement rule. In that rule, we
promulgated regulations for PALs in
response to comments received on draft
White Paper Number 3. As explained in
the preamble to the December 2002 final
rule, a PAL is an alternative approach
for determining NSR applicability on a
plantwide basis. Using PALs will allow
sources ‘‘to respond rapidly to market
changes,’’ and will ‘‘benefit the public
and the environment.’’ See 67 FR 80206.
Specifically, sources with PALs can
make changes without triggering the
major NSR preconstruction permitting
requirements, provided such changes
remain below the limit established in
their PAL and do not otherwise violate
the requirements of the PAL. A PAL is
an important technique that is
oftentimes used in tandem with flexible
permitting approaches such as advance
approvals and AOSs as described more
fully in this proposal.
The major NSR program applies to
‘‘major stationary sources,’’ which
include sources whose emissions
exceed certain thresholds established in
the statute, and to ‘‘major
modifications’’ at those sources, which
are modifications that exceed certain
significance levels established in EPA’s
regulations. Under minor NSR, an
owner or operator applies for a permit
to construct or modify a facility,
building, or other emissions unit, where
the new construction or modification
does not meet the emissions thresholds
10 In August 2000, based in large part on the
experience we gained through the pilot permit
program, we issued a draft guidance document
called White Paper Number 3, on which we
solicited comment. See White Paper Number 3, 64
FR 49803 (Aug. 15, 2000). That draft guidance
addressed various flexible permitting approaches,
including the use of the reasonably anticipated AOS
provision of 40 CFR 70.6(a)(9), Clean Buildings, and
PALs. We received comments on the proposed rules
and draft guidance and, in fashioning this proposal,
considered those comments that addressed advance
approval and AOSs as contained in 40 CFR
70.6(a)(9). As explained further below, we propose
a definition of ‘‘alternative operating scenario’’ and
certain other revisions to the part 70 regulations.
We also propose revisions to parts 51 and 52 that
provide for Green Groups.
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for major NSR. If the proposed
construction or modification is
approved, the permitting authority
issues a permit that contains emissions
limits and other appropriate terms and
conditions as necessary to protect the
NAAQS and the increments and to
assure consistency with the SIP.
Through our pilot experience, we
found that State minor NSR
requirements are among the most
important in designing a flexible air
permit for sources making frequent
physical and operational changes
because, absent an up-front
authorization for these changes, an
individual review and approval by the
permitting authority is typically
required before the changes can be
made. Any changes authorized under
minor NSR must be incorporated into
the title V permit along with permit
terms as necessary to assure compliance
with all applicable requirements (for
example, a MACT standard, which
would be applicable to the source in
addition to the ones addressed in the
advance approval issued under minor
NSR). The result is that the changes can
be implemented, under protection of the
permit shield, without any further
review or approval by the permitting
authority. In some cases, one or more
AOSs may be used to complement an
advance approval, for example where
the source anticipates varying operation
of the changed existing emissions unit
in a manner that would implicate a set
of applicable requirements different
from those of the minor NSR advance
approval, or where a different control
approach would not be effective until
and unless a particular change would be
made to an existing emissions unit.
Given the provisions of their minor
NSR programs, most of the States in
which EPA supported flexible permit
pilots (‘‘pilot States’’) believed that they
could issue construction approval for a
wide spectrum of changes using certain
boundary conditions established up
front in the minor NSR permit. The
actual conditions needed to accomplish
this varied depending upon the
requirements of the different State
minor NSR programs. A number of
techniques were successfully used in
pilot permits to authorize a category of
changes (i.e., a range of possible types
of changes, such as ‘‘any of various
physical changes to the rollers, drive
mechanism, and other components of
the coating section within a coating
line’’) under minor NSR, including
application of one or more plantwide
emissions caps, designation of an entire
process building or related activities as
the ‘‘emissions unit’’ for purposes of
minor NSR, and designation of an
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existing state-of-the-art emissions
capture and control system as fulfilling
State control technology requirements
(where they are applicable) for
authorized changes occurring over the
5-year term of the title V permit. Pilot
States, as part of granting advance
approvals under their existing minor
NSR programs, frequently required
sources to send a notice to the
permitting authority contemporaneous
with the operation of any entirely new
emissions unit relying upon the advance
approval.
A common technique for achieving
advance approval under minor NSR
found in the pilots was the presence of
one or more plantwide emissions caps.
These caps serve to limit the maximum
aggregate emissions associated with the
anticipated changes so as to protect
relevant ambient standards and
increments and to facilitate an advance
approval of a wide spectrum of changes
under minor NSR. They also serve to
limit the potential to emit (PTE) of the
source below certain applicability
thresholds in order to prevent
implication of otherwise potentially
applicable requirements (e.g., major
NSR) or to function as a PAL (in the
case of an existing major stationary
source).
III. What is the purpose of this action?
The Agency has learned a great deal
over the past decade through its pilot
permit program. In light of that
experience, the recent NSR
Improvement rule promulgated in
December 2002, and the comments we
received on the proposed revisions to
part 70 and draft White Paper Number
3, we propose revising the part 70 and
71 regulations and part 51 and 52
regulations.
As explained further below, the
proposed revisions to the operating
permit programs of parts 70 and 71 add
a definition and clarify requirements for
‘‘alternative operating scenario’’ (or
‘‘AOS’’) and add a definition for
‘‘approved replicable methodology’’ (or
‘‘ARM’’). The proposed revisions to the
major NSR program add a definition and
codify requirements for Green Groups.
The primary purpose of these
revisions to parts 70 and 71 is to build
upon the existing regulatory framework
and ensure that the flexible permitting
approaches with which we have
experience are more readily and widely
used. We recognize that many States’
minor NSR and part 70 programs may
already provide for the flexible
permitting approaches proposed and
that such States are currently able to
implement these approaches. Because of
the diversity of existing State minor
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NSR programs and our pilot experience
indicating the ability of many programs
to approve categories of future changes
in advance of making those changes, we
are not proposing any revisions to the
rules governing State minor NSR
programs at 40 CFR 51.160 through
51.164. By undertaking the part 70
rulemaking, it is not our intention to
preclude States from continuing to
develop and use flexible permit
approaches, where their current
regulatory structure provides authority
to do so. This rulemaking is instead
intended to encourage the use of
advance approvals where available and
appropriate, and to eliminate any
uncertainty that may exist with respect
to AOSs and to provide a clear
regulatory pathway governing flexible
air permit development in that area by
clarifying our 1992 part 70
regulations.11
The proposed revisions to parts 51
and 52 affecting major NSR programs
will increase options for flexible permits
under that program. Namely, the
proposed provisions for Green Groups
will offer operational flexibility options
for a defined section of a plant. This
option would augment the plantwide
strategy previously promulgated in the
NSR Improvement rule (i.e., PALs). The
proposed revisions would modify the
major NSR regulations in a limited way.
Consistent with the current NSR
requirements, we propose to clarify that
the definition of emissions unit would
allow a number of emission activities,
meeting certain criteria, to be treated as
a single emissions unit (i.e., a ‘‘Green
Group’’). We are proposing to change
the current NSR requirements to
11 Note that other approaches to AOSs and
advance approval may also be acceptable, although
they may not provide as much flexibility as the
approaches proposed. For example, some States
include in a title V permit a type of conditional
approval under which a source cannot construct or
operate otherwise approved changes until a minor
NSR approval is obtained for them. Essentially, this
approach creates in a title V permit a structure that
is a precursor to an AOS or an advance approval.
Once the minor NSR permit is issued, the source
can construct and operate the changes under the
conditional approval, but a title V permit revision
is needed to incorporate the now-available minor
NSR terms and to award the permit shield (where
available from the permitting authority). Where an
AOS is involved, this incorporation is also needed
to complete the AOS consistent with 40 CFR
70.6(a)(9). Our pilot permit experience suggests that
in many instances changes subject to minor NSR
can be approved in advance, although the ability for
a State to provide such approvals will vary
depending on the actual provisions of individual
State rules. As a result, where advance approval of
changes subject to minor NSR is available, we
encourage its incorporation into the title V permit
after or concurrent with obtaining the necessary
minor NSR approvals in order to provide a
permitting strategy with greater operational
flexibility, certainty, and permitting efficiency than
does a conditional approval approach.
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52211
provide expressly for Green Groups so
as to authorize in a major NSR permit
that emissions increases and changes
within such a group can occur over a
10-year period, provided the increases
and changes are authorized in advance
through major NSR and the emissions
activities associated with the Green
Group are controlled to the level
determined to be BACT/LAER. Also, the
requirements of 40 CFR 52.21(j)(4) and
51.166(j)(4) requiring reevaluation of
BACT for phased construction projects
and of 40 CFR 52.21(r)(2) requiring
continuous construction to commence
within 18 months would not apply to
NSR permits involving Green Groups.
We believe that these proposed
revisions will increase operational
flexibility, while ensuring
environmental protection and
compliance with applicable
requirements. Moreover, based on our
pilot experience, we anticipate that
these revisions will promote improved
environmental performance, although
we recognize that the nature of the
improvements will depend on the
numbers and types of sources that opt
to use the flexible permitting
approaches described in this document.
IV. What experience did we gain from
the 14-year pilot permit program?
This section summarizes the benefits
of the pilot permits; includes an
overview of the sources’, permitting
authorities’, and our conclusions
concerning the effectiveness of the pilot
permits; and presents our
recommendations regarding public
participation in flexible permitting.
Through the pilot permit program,12
which began in 1993, we sponsored
various projects, including projects
undertaken through the Agency’s
‘‘Pollution Prevention in Permitting
Program’’ (P4). The pilot program
generally involved the issuance of
flexible air permits designed to
accommodate operational flexibility.
The pilot permits facilitated
operational flexibility by first obtaining
advance approval under NSR.
Frequently the authorizations involved
changes that were to occur under a PAL
or other facility-wide cap on emissions
which, once approved by the relevant
permitting authority, served both to
assure that major NSR would not be
12 Sources at the following locations participated
in our pilot permit program: (1) 3M (St. Paul, MN);
(2) Intel (Aloha, OR); (3) Lasco Bathware (Yelm,
WA); (4) Imation (Weatherford, OK); (5) Cytec
(Connecticut); (6) DaimlerChrysler (Newark, DE); (7)
Merck (Elkton, VA); (8) Merck (Barceloneta, PR); (9)
Saturn (Spring Hill, TN); (10) BMW (Spartanburg,
SC); (11) Eli Lilly (West Lafayette, IN); (12) 3M
(Nevada, MO); and (13) Imation (Camarillo, CA).
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applicable to changes occurring under
the cap and to assure that ambient
standards would be protected consistent
with the requirements of minor NSR.13
These caps were then incorporated into
the title V permit with appropriate
permit terms and conditions. In most
cases, once these caps were
incorporated into a title V permit,
sources did not need to seek additional
approvals from the title V permitting
authority prior to implementing the
changes authorized under the caps. As
necessary, the title V permit would also
contain additional terms and conditions
needed to assure compliance with any
other applicable requirements applying
to such changes.
As noted above, following issuance of
the pilot permits, we conducted an indepth review of six of the permits.14 In
selecting the permits to review, we
focused our evaluation on those pilots
with sufficient implementation
experience to provide a reasonable
historical record of performance, and we
continue to believe that these pilots
represent a sufficiently diverse reference
point from which to judge the
effectiveness of flexible air permits over
a broad range of sources. Those reviews
involved: (1) Detailed analyses of the
sources’ and permitting authorities’
experiences developing and
implementing the pilot permits; (2) a
thorough review of information
available in the public record at the
permitting authority; (3) discussions
with source personnel; (4) site visits to
the source and meetings with permitting
authorities; and (5) independent
verification of compliance status and
data collection and management
techniques, including recordkeeping
and related requirements.
Our analyses revealed several benefits
of the flexible permitting approaches
used in the pilots, and those benefits are
summarized briefly below. We invite
comment on any similar or different
experiences others have had in piloting
flexible air permits, particularly where
13 The VOC emissions caps used in the pilots
were determined to be adequate for purposes of
safeguarding the ozone NAAQS, but for other
pollutants (e.g., air toxics) States sometimes
required a replicable modeling procedure to screen
the impacts of individual emissions increases
relative to acceptable ambient toxics levels. Here an
ambient dispersion model, complete with
implementation assumptions, is approved into the
minor NSR permit to evaluate any new pollutant of
concern or increased existing pollutant emissions.
Failure of a particular change to meet the screening
levels triggered the need for case-by-case review of
that change from the permitting authority.
14 The six permits that we analyzed were: (1) Intel
(Aloha, OR); (2) 3M (St. Paul, MN); (3) Lasco
Bathware (Yelm, WA); (4) DaimlerChrysler
(Newark, DE); (5) Saturn (Spring Hill, TN); and (6)
Imation (Weatherford, OK).
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these experiences are relevant to this
rulemaking.
A. What were the benefits of the pilot
permits?
This section provides an overview of
the environmental, informational,
economic, and administrative benefits
of the flexible pilot permits. For
additional information on these and
other benefits of the pilot program,
please refer to the ‘‘Evaluation of the
Implementation Experience with
Innovative Air Permits,’’ which
documents all of our findings
concerning the six pilot permits that we
evaluated.15
1. Environmental Improvements
Achieved Using Flexible Permits
In our evaluation, we documented
several environmental performance
benefits of the flexible pilot permits,
including that the permits facilitated
emissions reductions and increased P2
efforts. In particular, as discussed
further below, the emissions cap
framework in the flexible permits
enabled significant reductions in actual
plantwide emissions and/or emissions
per unit of production. For example, of
the five sources that had operated under
their flexible permits for 3 or more
years, all five achieved 30-to 80-percent
reductions in actual plantwide
emissions and/or emissions per unit of
production. Actual emissions from the
sixth source were reduced by 27 percent
in the first year of operation under its
flexible permit, but it is difficult to draw
conclusions based on a single year of
data. One company, using P2, lowered
its actual volatile organic compound
(VOC) emissions by 70% (from 190 tons
per year (tpy) to 56 tpy), while
increasing production. This allowed the
facility to commit to keeping its VOC
emissions below the major source
threshold (i.e., become a ‘‘synthetic
minor’’ source) so that it was no longer
subject to major NSR. Another company
lowered its actual VOC emissions from
1,400 tpy to less than 800 tpy, primarily
through P2 associated with vehicle
coatings and plant solvent usage.
We attribute the environmental
performance improvement benefits of
the flexible permits to several factors.
First, several companies reported that
the emissions caps had a ‘‘focusing
effect,’’ drawing company personnel(s
attention on how to manage most
effectively all of the activities within the
15 Among other things, the report confirmed that
the flexible permits are enforceable in a practical
manner by EPA and permitting authorities. See
Report at pages 5, 20. See footnote 9 of this
preamble for information on how you can obtain
the report.
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plant, even those not subject to
regulation, in an effort to minimize total
plantwide emissions.16 An emissions
cap also creates incentives for
companies to pursue additional
emissions reduction opportunities to
increase the margin of compliance,
which is the difference between the
level of the emissions cap and the
source’s actual total plantwide
emissions. Larger compliance margins
typically reduce the risk of
noncompliance with an emissions cap
and create room under the cap to
accommodate future emissions
increases related to production or other
operational changes. The cap on
emissions from the plant, which is set
during permitting at a level judged to be
environmentally protective, ensures that
such future emissions increases together
with existing emissions will not exceed
this protective level. To obtain a
sufficient margin of compliance with
these caps, sources frequently
voluntarily controlled emissions on
grandfathered units, which are units
that would otherwise not be subject to
control, and increased the stringency of
control on regulated units.
Additionally, we found that the use of
advance approvals and AOSs improved
operational efficiency at the plants
because companies knew in advance
what changes were authorized, making
resource allocation more efficient and
accommodating the typically
incremental, iterative nature of
industrial process improvements. We
also found that P2-related projects
became more attractive to the
companies when advance approved
because such projects could be
undertaken without the delay and
uncertainty of future case-by-case
approvals. In addition, P2-related
projects reduced emissions and enabled
sources to comply more easily with
emissions limits such as plantwide
emissions caps.
2. Informational Benefits Achieved
Using Flexible Permits
We have consistently maintained that
including advance approvals and AOSs
in a title V permit ensures that the
permit presents a complete
representation of the operations of the
permitted facility. See 57 FR 32276; July
21, 1992. By requiring information
concerning flexible permits as part of
the permit application, EPA and the
permitting authorities are better able to
assess, in aggregate, all proposed
operations and, more significantly, to
16 See the pilot permit report, ‘‘Evaluation of the
Implementation Experience with Innovative Air
Permits,’’ page 22.
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determine all relevant applicable
requirements and to include in the draft
permit terms and conditions for each
approved scenario to assure compliance
with those applicable requirements and
the requirements of part 70. By
comparison, conventional permitting
approaches provide for a more narrow,
case-by-case view of facility
modifications, soliciting comment only
on the specific change proposed and
requiring individual permitting actions
in response to each request by the
permittee for a change in the permit.
Our pilot experience confirmed the
significant value of presenting a
comprehensive picture of a source(s
operations over the term of the title V
permit. Specifically, we found that with
proposed flexible permits involving
changes under a PAL or other emissions
cap, permitting authorities were better
able to understand the scope of planned
changes at the source and the
maximum, cumulative environmental
effects of those changes. In addition, the
flexible permit applications provided
increased information to permitting
authorities and the public in areas such
as plantwide emissions performance
and P2 activities, as compared to
information typically available under
conventional permit approaches.
Likewise, permitting authorities
indicated that on balance, flexible air
permits enhanced the availability of
information to the public during permit
implementation.
Moreover, through the pilots, we
found that early public outreach and
involvement can be very useful in
situations where new permitting
techniques have not previously been
used in a particular jurisdiction. We
encourage permitting authorities to
consider early outreach and public
involvement when implementing such
permitting techniques until the
techniques become more widely used
and public familiarity with them
increases, recognizing that other factors
(e.g., permit complexity) should factor
into the permitting authority(s
consideration of supplemental public
outreach efforts.
Our evaluation of the six pilot permits
also revealed the importance of
reporting related to plantwide
applicability limits. The type of
reporting required in several of the
flexible permits is now codified in the
PAL provisions of the December 2002
NSR Improvement rule.
3. Economic Benefits Achieved Using
Flexible Permits
Participating companies in the pilot
program reported that a flexible air
permit significantly reduces the
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uncertainty and transaction costs
associated with the title V permitting
process because the source obtains
approval of the changes it reasonably
anticipates implementing during the 5year term of the permit at one time.
Based on our evaluation of the six pilot
permits, we found that the increased
certainty and reduced transaction costs
improved participating companies’
ability to compete effectively in the
market and enabled them to retain, and
in some cases, create jobs. For example,
one company reported that its pilot
permit allowed it to remain highly
responsive to the marketplace and
thereby avoid either lost sales and/or
permanent loss of market share. An
automotive company indicated that its
flexible permit was a principal factor in
the plant’s selection to manufacture an
engine model to be used in the
company’s global vehicle assembly
operations, leading to the creation of
700 jobs. The permit helped the plant
secure the engine contract because it
enabled the plant to reduce the project
time line for production of the new
engine to 24 months and to
accommodate future changes with
minimal delay.17
Several companies also indicated that
obtaining authorization of reasonably
anticipated changes improved the
predictability of change implementation
time frames for project planning and
avoided what can be substantial
opportunity costs. For example, one
company reported that its flexible
permit likely saved hundreds of
business days associated with making
operation and process changes to ramp
up production for new products,
respond to market demands, and
optimize production processes. Industry
estimates of the opportunity costs of
production downtime and time delays
run as high as millions of dollars in just
a few days due to lost sales and other
factors.18
Notwithstanding that the
implementation of flexible air permits
often was associated with more
production-related jobs, pilot companies
also reported that flexible air permits
significantly reduced permit-related
staff time and related resource costs
because there was no longer a need to
seek and process multiple case-by-case
permit actions because the changes
reasonably anticipated at the facility
were already included and approved in
17 See ‘‘EPA Flexible Permit Implementation
Review: Saturn Permit Review Report,’’ pages 9 and
34, which is available at https://www.epa.gov/ttn/
oarpg/t5/memoranda/iap_sprr.pdf.
18 Findings are discussed in more detail in the
‘‘Evaluation of Implementation Experiences with
Innovative Air Permits’’ report, under Finding 8.
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52213
the permit. For example, an automotive
company estimated that it saved
approximately 505 hours of staff time
during its initial flexible permit term.
Another pilot company reported permitrelated staff time savings of 1,200 to
1,600 hours per year during its initial
title V permit term. In both cases,
companies reported that the time
savings enabled environmental
personnel to focus more time and
attention to other environmental
management activities, including P2.
Companies further indicated that the
time necessary to record changes in
operating scenarios in the on-site log, as
required by 40 CFR 70.6(a)(9), was
significantly less than the permit-related
staff time necessary to prepare permit
applications under a general change-bychange permitting approach.
4. Administrative Benefits Achieved
Using Flexible Permits
Our pilots evaluation found that the
flexible permits resulted in a net cost
savings both for the source, as noted
above, and for the permitting authority.
We specifically found that the resources
permitting authorities expended on
processing permitting applications
under title V and the NSR programs
were reduced under the pilot program,
since the operational flexibility
provisions, like 40 CFR 70.6(a)(9),
eliminated the need to submit a permit
application for each operational change.
For example, one permitting authority
estimated that each facility change made
pursuant to a flexible permit saved the
permitting authority approximately 20
to 40 hours in staff time that otherwise
would have been incurred had the
facility, instead of obtaining the advance
approvals and AOS, sought title V
permit modification on a change-bychange basis. In fact, permitting
authorities reported that the
administrative cost savings during
implementation of the pilot flexible
permits indicate that increased use of
flexible permitting will enable them to
reduce permitting backlogs and to focus
resources on other higher priority
environmental needs.
These cost savings must be put in
context of a higher front-end cost to
design an acceptable permit approach to
pilot (a cost that should decrease as
more experience with flexible permits
occurs in tandem with a better defined
policy). The two participating
permitting authorities that attempted to
quantify this effect believed that, even
with the higher front-end design costs
associated with their pilot, the initial
experience suggested there would be a
net reduction in the overall
administrative costs associated with
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these permits after 2–3 years of
implementation. We believe that the
administrative benefits achieved for the
evaluated pilot permits are broadly
indicative of the benefits generally
available from flexible air permits. In
fact, as flexible air permitting becomes
more mainstream, we expect the frontend costs to design such permits to be
reduced, resulting in faster recouping of
these expenses and greater benefits over
time.
jlentini on PROD1PC65 with PROPOSALS2
B. What were the conclusions of the
sources, permitting authorities, and EPA
about flexible permits?
The sources that obtained a flexible
air permit maintain that such a permit
is a valuable business asset. These
sources regularly relied upon the
operational flexibility provided in the
permit to take advantage of
opportunities in the market place. These
sources also indicated that the following
circumstances heightened the need for
and benefits achieved using a flexible
air permit:
• Short time frames for bringing new
products to market (time-to-market
needs).
• Need to accommodate rapid shifts
of product lines, processes, and
production levels to enable optimal
asset utilization in a company’s network
of facilities.
• Active advanced manufacturing
programs (e.g., lean manufacturing, Six
Sigma, agile manufacturing) that require
rapid and iterative changes to
operations and equipment.19
• Anticipated renovation or
expansion projects.
• Active P2 programs with continual
process improvements.
The permitting authorities in the pilot
program concluded that the permits
provided significant environmental
19 These manufacturing concepts have been
defined in various ways. Generally, however, lean
manufacturing is defined as an initiative focused on
eliminating all waste in manufacturing processes.
Principles of lean manufacturing include zero
waiting time, zero inventory, scheduling (internal
customer pull instead of push system), batch to
flow (cut batch sizes), line balancing, and cutting
actual process times. Six Sigma is defined as a
rigorous and disciplined methodology that utilizes
data and statistical analysis to measure and improve
a company’s operational performance, practices,
and systems. Six Sigma identifies and prevents
defects in manufacturing and service-related
processes. In many organizations, it simply means
a measure of quality that strives for near perfection.
Agile manufacturing emphasizes the ability to
thrive and prosper in an environment of constant
and unpredictable change and includes the use of
tools such as rapid prototyping, rapid tooling, and
reverse engineering to address customers who
require small quantities of highly custom, designto-order products, and where additional services
and value-added benefits like product upgrades and
future reconfigurations are as important as the
product itself.
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performance and administrative
benefits. They also expressed support of
flexible permitting techniques as a
permitting option. The permitting
authorities believed that flexible permits
are particularly effective when applied
to sources with demonstrated
operational change needs and the
operational and technical capacity to
meet all relevant requirements
associated with advance approvals,
AOSs, PALs, and other operational
flexibility provisions.
In general, based on our pilot
experience, we believe that sources with
certain characteristics are the ones that
can both meet the requirements of
operational flexibility provisions and
benefit from them. These characteristics
include: A strong compliance history,
maintenance of a well-documented and
effective environmental management
system, commitment to continuous
environmental improvement,
attentiveness to P2, ability to track and
manage operational changes and
emissions, and the existence of good
community relations. The types of
sources that exhibit these characteristics
typically include, for example, the
members of EPA’s National
Environmental Performance Track
Program (see https://www.epa.gov/
performancetrack/) and similar State
environmental leadership programs.
Our Performance Track program
illustrates our ongoing commitment to
reward and recognize exemplary
environmental performance.
We currently intend to allocate our
implementation resources for the final
rule on a priority basis to assist
Performance Track facilities that wish to
obtain flexible air permits. More
specifically, we intend to deploy
resources and tools designed to assist
Performance Track facilities in their
efforts to capture the opportunities
provided through flexible air permits.
Our efforts to facilitate the
implementation of flexible permits
could include, for example, education
and outreach components that would
allow Performance Track members to
assess the costs and benefits of a flexible
permit. We also intend to provide EPA
technical resources and expertise
through identified points of contact to
facilitate the resolution of technical and
other issues (should any arise)
associated with implementing a flexible
air permit at a Performance Track
facility. We encourage State permitting
authorities to consider a similar
prioritization of resources when issuing
flexible air permits to sources that are
similarly situated to Performance Track
companies.
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C. What are EPA’s recommendations for
public participation in flexible
permitting?
Based on our experience with pilot
permits, we believe that flexible permits
provide at least as much environmental
protection as conventional permits and
promote superior environmental
performance. Nevertheless, we also
recognize that flexible permits will
contain features, such as AOSs, ARMs,
advance approval of minor NSR, or
Green Groups, that may not be familiar
to the reviewing public. For this reason,
we recommend that permitting
authorities consider using their
discretion to enhance the public
participation process when warranted
for a particular flexible permit. Some
ideas for doing so are described below.
During the permitting process,
permitting authorities could consider
making the permit application available
to the public soon after receipt. We
found for these pilot permits that early
outreach to the community, rather than
waiting until the draft permit was
prepared, was an effective public
participation strategy.
The minimum public comment period
required for a title V permit renewal or
significant permit modification is 30
days. Where a significant amount of a
permit’s content consists of terms to
incorporate operational flexibility, we
suggest that you consider expanding the
comment period to 45 days or more.
Note, however, that for some of our pilot
permits, early outreach to the public
was sufficient to resolve community
questions and comments early in the
process, so that by the time of the public
hearing and comment period no adverse
comments were received.
Finally, in order to ensure adequate
technical support and accessibility for
the public in their efforts to understand
and comment upon flexible air permits,
we suggest that States provide a
principal point of contact for
responding to technical questions and
ensure the availability of draft permits,
applications, and technical support
documents on an Internet Web site. We
believe that any additional costs here
will be offset by the subsequent
administrative cost savings to the
permitting authority resulting from the
reduced need to process permit
revisions for sources with flexible
permits.
V. What are the key elements of this
proposal?
This section summarizes the key
elements of this proposal. A more
detailed discussion of these elements as
well as other proposed regulatory
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changes are provided below in sections
VI and VII.
jlentini on PROD1PC65 with PROPOSALS2
A. What are the key elements of
proposed revisions to parts 70 and 71?
There are several key regulatory
revisions that we are proposing to parts
70 and 71. First, we are proposing to
modify 40 CFR 70.6(a)(9) generally to
refer to ‘‘alternative operating
scenarios,’’ as opposed to ‘‘operating
scenarios.’’ In addition, we are
proposing to define the term
‘‘alternative operating scenario (AOS)’’
and codify certain requirements
described in this proposal for AOSs.
Specifically, we propose to define
‘‘alternative operating scenario (AOS)’’
as a scenario authorized in a part 70
permit that involves a physical or
operational change at the part 70 source
for a particular emissions unit, and that
subjects the unit to one or more
applicable requirements that differ from
those applicable to the emissions unit
prior to implementation of the change or
renders inapplicable one or more
requirements previously applicable to
the emissions unit prior to
implementation of the change.
This document also discusses our
proposal for ‘‘approved replicable
methodologies’’ (ARMs) and the way in
which they may be approved into the
title V permit by the permitting
authority. We are proposing to define an
ARM as part 70 permit terms that: (1)
Specify a protocol which is consistent
with and implements an applicable
requirement, or requirement of part 70,
such that the protocol is based on sound
scientific/mathematical principles and
provides reproducible results using the
same inputs; and (2) require the results
of that protocol to be used for assuring
compliance with such applicable
requirement or requirement of part 70,
including where an ARM is used for
determining applicability of a specific
requirement to a particular change. An
ARM, however, cannot modify an
applicable requirement in any way. As
explained further below, an ARM can be
particularly useful in facilitating the
implementation of advance approvals
and AOSs, but can also be used
independent of them.
Also in this document, we are
proposing that a source include in its
semi-annual monitoring reports under
40 CFR 70.6(a)(3)(iii) information
relating to any AOS and/or ARM
implemented during the reporting
period. This information should help
permitting authorities remain informed
as to which AOSs and ARMs in the title
V permit are being implemented at the
site and at which time.
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We are not proposing revisions to any
applicable requirement (other than
revisions to parts 51 and 52 providing
for Green Groups—see section VII
below) in order to facilitate advance
approvals. As mentioned above, our
pilot experience confirms that obtaining
advance approval under minor NSR is
often a critical element in the design of
a flexible air permit. This experience
also suggests that many State minor
NSR programs may already provide the
legal authority necessary to issue minor
NSR permits that accommodate various
types of operational flexibility which
can be readily incorporated into title V
permits. We are therefore not proposing
any revisions to the minor NSR
regulations. Nonetheless, we encourage
States to implement advance approvals
in response to requests by sources under
their existing minor NSR programs as
appropriate and to seek additional
authority where they do not currently
have such discretion. Based on our pilot
experience, we also believe that the
ability to advance approve a particular
change with respect to other applicable
requirements requiring a specific
authorization can often be determined
without further regulatory changes.
Similarly, we are not proposing to
revise part 70 to address how advance
approvals might be accomplished. We
believe that part 70 already requires
incorporation of the terms in a permit
issued to advance approve changes
under certain applicable requirements.
For example, permit terms contained in
a State’s minor NSR permit are
themselves deemed to be applicable
requirements as defined in section 70.2
and, as such, are to be included in the
title V permit for the relevant source.
Frequently, however, the permitting
authority may need to augment the
terms of NSR permits authorizing the
advance approval of certain changes in
order that these changes can be made
without further review or approval.
These terms would be added as
necessary to assure compliance with
other applicable requirements also
implicated by the advance approved
changes which were unaddressed in the
specific authorizations obtained for
them. As would be the case for any
other applicable requirement, the part
70 permit must meet the requirements
of part 70 (e.g., monitoring, reporting,
and compliance certification) with
respect to advance approvals. When the
title V permit terms relating to advance
approvals are effective, then the changes
which were advance approved would
occur under protection of the permit
shield (where available and granted by
the permitting authority).
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52215
B. What are the key elements of
proposed revisions to parts 51 and
52? 20
With this document, we propose
adding a definition of ‘‘Green Group.’’
We also propose to add monitoring,
recordkeeping, reporting, and testing
safeguards applicable to Green Groups
to enhance the availability of
information and ensure that these
groups function as intended.
A Green Group consists of designated
emissions activities that are ducted to
one common air pollution control
device that is determined to meet BACT
or LAER, as applicable, for the entire
group of emissions activities taken as a
whole. A Green Group is, by definition,
a single emissions unit for purposes of
major NSR. In addition to designated
existing emissions activities, a Green
Group may include changes (e.g.,
reconfiguration and/or expansion) to
these existing activities and/or the
addition of new emissions activities
ducted to the control device, either of
which could result in an increase in
capacity and a significant increase in
actual emissions. To establish a Green
Group, the source must go through the
major NSR permitting process and
obtain a permit. To protect the NAAQS,
PSD increments, and Class I areas, the
proposed rules require an annual
emissions limit and any necessary shortterm limits for the Green Group, as well
as comprehensive monitoring, reporting,
recordkeeping, and testing under NSR
for Green Groups to assure compliance
with the limit(s).21
VI. What changes are we proposing to
parts 70 and 71?
We are proposing revisions to parts 70
and 71 to build upon the existing
framework in 40 CFR 70.6(a)(9), which
authorizes AOSs. As discussed below in
section VI.A, we are proposing to add a
definition for AOS and to provide for
the use of consistent terminology for
AOSs. In section VI.B, we describe the
information that the source must
provide in a title V permit application
under 40 CFR 70.5(c) when seeking
approval of an AOS, and in section VI.C
we discuss the terms that must be
included in a title V permit for an AOS
and for an ARM. Section VI.D presents
two examples of flexible permits using
20 Although we are proposing certain revisions to
the major NSR program, we are proposing no
changes to any other applicable requirement, as that
term is defined in 40 CFR 70.2.
21 The NAAQS and increments for some
pollutants are established over short-term periods
as well as annually. For example, annual, daily, and
3-hour NAAQS and increments are defined for
sulfur dioxide. Accordingly, some NSR permits
include emissions limits for these shorter periods.
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AOSs. In section VI.E, we address
additional issues related to AOSs, and
in section VI.F we detail the minor
differences between the proposed
revisions for part 70 and part 71. In the
case of both AOSs and ARMs, the State
must have sufficient authority to grant
them if proposed by a source, but the
permitting authority retains the
discretion as to the appropriateness of
doing so on a case-by-case basis,
depending on the specific facts of the
situation.
A. What is our proposed definition of an
AOS, and how does it provide a source
operational flexibility?
As mentioned previously, the concept
of an AOS is not a new one. Under
existing 40 CFR 70.6(a)(9), a source may
request in its permit application that the
permitting authority approve reasonably
anticipated operating scenarios. If the
permitting authority determines that the
proposed operating scenarios are
consistent with the requirements of part
70 and approves them, it would include
those scenarios in the source’s part 70
permit, and the source may implement
them without further review or
approval. Fundamentally, the
permitting authority must ensure that
the proposed operating scenarios are
adequately described such that all
applicable requirements associated with
each scenario are identified and
appropriate terms and conditions to
assure compliance with these
requirements are included in the permit.
In addition, the permitting authority
must ensure that the source obtained all
specific authorizations required under
any applicable requirements (primarily
those under minor NSR). The provisions
of 40 CFR 70.6(a)(9) were promulgated
consistent with section 502(b)(6) of the
Act, which mandates the streamlining of
the application and permitting
processes.
There may be situations where a
permitting authority does not approve
an AOS which has been proposed by a
source for a particular emissions unit.
For example, a permitting authority may
reject an AOS proposed by a source if
it determines that the source’s
description of the scenario is
insufficient to identify all applicable
requirements or craft appropriate terms
and conditions to ensure compliance
with applicable requirements, or if
required authorizations under
applicable requirements triggered by the
AOS have not been obtained.
To clarify our intent regarding AOSs,
we propose the following definition at
40 CFR 70.2:
Alternative operating scenario (AOS)
means a scenario authorized in a part 70
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permit that involves a physical or operational
change at the part 70 source for a particular
emissions unit, and that subjects the unit to
one or more applicable requirements that
differ from those applicable to the emissions
unit prior to implementation of the change or
renders inapplicable one or more
requirements previously applicable to the
emissions unit prior to implementation of the
change.
Thus, the change at the part 70 source
must be physical or operational in
nature and must either subject a
particular emissions unit to at least one
new applicable requirement or
eliminate at least one requirement that
applied to the unit prior to the change.
In addition, the change, in order to be
eligible for an AOS, must be allowable
under all applicable requirements.22 For
example, a change allowed under an
applicable MACT standard but also
subject to minor NSR would not be
eligible for inclusion in an AOS until
the source obtains the necessary
preconstruction approval. That is, the
source requests and obtains from the
permitting authority a minor or major
NSR permit, as applicable, authorizing
the change to occur, and the terms of the
NSR permit are then incorporated into
the source’s title V permit as part of an
AOS. We are proposing this definition
not to change the current requirements
for AOSs but rather to foster a common
and consistent understanding of the
types of situations that AOSs can
address.
The types of physical or operational
changes which could trigger an AOS can
vary widely. Such changes potentially
encompass a wide spectrum of activities
undertaken by a source which cause one
or more applicable requirements to
apply (or to no longer apply) to the
emissions unit undergoing the change.
Nonetheless, these changes must be
consistent with any limitations
contained in applicable requirements
that are triggered. Thus, anticipated
physical and operational changes must
be described adequately to identify the
applicable requirements.
In some cases, physical or operational
changes may be exempt from certain
22 Failure to anticipate and include a particular
change under an AOS does not in and of itself bar
the source from implementing the change if it can
satisfy the requirements of the off-permit provisions
in part 70, such as those set forth at 40 CFR
70.4(b)(12) and (b)(14). The permit shield does not
extend to changes made pursuant to these
provisions. See, e.g., 40 CFR 70.4(b)(12)(i)(B),
(b)(12)(ii)(B), (b)(14)(iii). For example, during the
term of its part 70 permit, a source might obtain
approval under minor NSR to construct and operate
a new emissions unit. Where available and granted
by the permitting authority, the source can
implement the change under the off-permit
provisions, assuming that the change is not
addressed or prohibited by the terms of the source’s
part 70 permit.
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applicable requirements but not from
others. For example, the New Source
Performance Standards (NSPS) and
major NSR regulations specifically
exempt from their purview certain types
of changes, such as those that do not
reach the threshold for a
‘‘modification.’’ These same changes,
however, could still implicate other
applicable requirements. For example, a
switch to another fuel which a unit is
already capable of accommodating
could trigger a SIP requirement or a
Maximum Achievable Control
Technology (MACT) standard, while
being exempt from NSPS and major
NSR. Such SIP and MACT requirements
must, therefore, be identified as
applicable requirements in an
application for an AOS governing the
fuel switch.
Under this proposal, activities that do
not involve a physical or operational
change to the regulated equipment do
not constitute an AOS, even when such
change is made to switch between
compliance options provided for in an
applicable requirement. For example,
suppose a source chooses to switch
between the compliance options
allowed under an applicable
requirement (e.g., a MACT standard or
NSPS). Under the Printing and
Publishing Industry MACT standard (40
CFR part 63, subpart KK), a product and
packaging rotogravure affected source
that uses compliant inks and coatings
(i.e., inks and coatings with low HAP
content) may demonstrate compliance
for each month by any one of six
compliance options set out in the
standard. Each of the compliance
options involves slightly different
applicable requirements in that different
characteristics of the inks and coatings
must be tracked and different
calculations must be carried out
monthly to demonstrate compliance.
We propose that a source may switch
between such compliance options
without including AOSs for each
compliance option in its permit. Rather,
the compliance options may simply be
included in the permit as alternative
requirements of the applicable standard.
We acknowledge, however, that this
approach may raise issues regarding
whether an operational change at the
source has triggered the change in the
compliance option. For example,
subpart KK also provides for
compliance options that use an add-on
control device rather than compliant
inks and coatings. If a source alternates
between compliant materials (using one
of the six associated compliance
options) and noncompliant materials
(complying through use of a thermal
oxidizer), should this be characterized
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primarily as a shift for compliance
purposes that does not require an AOS
in the permit, or as an operational
change requiring an AOS? What if the
source alternates among the compliance
options for compliant inks and coatings
based on the characteristics of the
materials that it uses in each month? We
request comment on the issue of
whether a switch from one compliance
option to another is better characterized
as allowable under an applicable
requirement or as a physical or
operational change that triggers a
different applicable requirement and
therefore requires an AOS. Regardless of
the approach ultimately adopted, we
strongly recommend that permitting
authorities and sources work together to
include in the permit those compliance
options allowed under the applicable
requirement that a source may
reasonably anticipate using during the
term of the permit. Whether
incorporated as AOSs or simply as
compliance alternatives, we believe that
a title V permit can be fashioned to
allow a source to switch between
compliance options without needing a
permit revision to do so.
The second criterion for a shift in
operating scenario under this proposed
definition is that the triggering change
must cause: (1) At least one applicable
requirement to apply which was not in
effect before the change; and/or (2) at
least one applicable requirement to no
longer apply as a result of the change.
‘‘Applicable requirement’’ as defined in
40 CFR 70.2 includes all the separate
emissions reduction, monitoring,
recordkeeping, and reporting
requirements of a particular standard or
SIP regulation and all the terms and
conditions of preconstruction permits
issued pursuant to regulations approved
or promulgated through rulemaking
under title I of the Act.
As such, AOSs can be quite effective
where existing units at sources simply
make physical or operational changes
that do not require any advance
approval, but they nonetheless
implicate one or more different
applicable requirements. This may
occur, for example, where an existing
boiler is permitted to combust different
fuels, which implicate different sets of
applicable requirements. We elaborate
on this situation below in section VI.D,
Example 1. Example 2 in that section
presents a situation where AOSs are
used in conjunction with advance
approvals.
Under the second criterion above,
AOSs are often separate and distinct
from advance approvals. For example,
we propose that the addition of a new
emissions unit pursuant to an advance
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approval does not require an AOS,
unless the particular unit, once
operational, requires the flexibility to
make subsequent physical or
operational changes that will cause
applicable requirements to apply that
are different from those applicable to
the authorized baseline scenario for the
new unit upon operation. We believe
that construction and operation of a new
unit authorized in an advance approval
does not represent a shift in operating
scenario for the unit, but rather
represents beginning its initial or
baseline operation.23 However, we
solicit comment on whether such new
unit additions should instead be
characterized as AOSs.
Similarly, incorporation in a part 70
permit of an advance approval
contained in an authorizing NSR permit
for a physical or operational change to
an existing emissions unit frequently
would not require an accompanying
AOS, where the terms of the NSR permit
containing the advance approval are
effective for the unit upon issuance of
the part 70 permit. For example,
suppose a source, in the process of
renewing its part 70 permit, obtains a
minor NSR permit that advance
approves a change to an existing
emissions unit, and the NSR permit
includes new requirements (such as an
increased level of control and associated
MRRT) that do not currently apply to
the unit in its baseline operations. If the
source agrees to include the new NSR
requirements in its part 70 permit
effective upon issuance and, notably,
prior to making the authorized change,
no AOS is needed to supplement the
advance approval.24 This is because no
applicable requirements will begin to
apply, or cease to apply, when the
authorized change is subsequently
implemented. One or more AOSs,
however, would be needed in the permit
if the source wishes to build in the
flexibility to make subsequent physical
or operational changes at the emissions
23 An advance approval that is incorporated into
a part 70 permit remains subject to all the
conditions of the underlying authorization. For
example, if an underlying minor NSR permit is
contingent upon the source commencing
construction of the authorized change(s) within a
certain period, the authorization in the part 70
permit also will lapse if the source fails to meet the
required deadline. The source is responsible for
obtaining any extensions or additional
authorizations as necessary to keep the advance
approval in the part 70 permit in effect.
24 If any other applicable requirements would be
triggered by the change that are not addressed by
the minor NSR advance approval, they also must be
included in the part 70 permit and become
applicable upon its issuance. Alternatively, such
requirements may be prevented from applying
through limits contained in the permit (e.g., a PAL
or PTE cap(s)).
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unit that would trigger new applicable
requirements or cause existing
requirements to no longer apply.
In contrast, the proposed definition of
AOS does include scenarios where the
new applicable requirements implicated
by advance approved changes at
existing units are not effective until the
source actually makes the change. For
example, an advance approval might
authorize modifications to an existing
process line under minor NSR, provided
that the source meets an NSPS
applicable to the line upon its
modification. Alternatively, we also
propose that this situation could be
characterized as an authorized advance
approval that does not require
incorporation of an AOS into the part 70
permit. That is, no AOS would be
required where implementation of an
authorized change irreversibly triggers
the new applicable requirement(s), such
that the emissions unit cannot return to
its baseline status in the future. As such,
this scenario is the creation of a new
baseline scenario, analogous to the
addition of a new emissions unit. We
solicit comment on this issue and the
two approaches we have proposed. We
also solicit comment in general on our
proposal to distinguish from AOSs all
advance approvals, including those
involving the addition of new units.
In addition to proposing a definition
of AOS, we are also clarifying the
regulations, because the regulations use
inconsistent terminology when referring
to AOSs. See e.g., 40 CFR 70.4(d)(3)(xi)
(referring to ‘‘(alternate scenarios’’). For
consistency purposes, we propose to use
the term ‘‘alternative operating
scenarios’’ (or AOSs) throughout the
regulations when referring to an
alternative operating scenario under 40
CFR 70.6(a)(9). See proposed 40 CFR
70.4(d)(3)(xi) and 40 CFR 70.5(c)(2) and
(7). Note also that any specific ‘‘AOS’’
listed in a permit refers to a specific
operating scenario which differs
importantly from the previous scenario
(also contained in the permit) in that
one or more different applicable
requirements are implicated by the shift
in operating scenarios. The scenario that
reflects the current operations and
applicable requirements of the source at
the time of permit issuance is called the
‘‘baseline scenario.’’
A key objective for a source
requesting an AOS is to identify and
describe in the title V permit
application those changes that are
reasonably anticipated to occur for each
emissions unit during the term of the
title V permit. This proposal clarifies
that AOSs can be used to provide
operational flexibility for a variety of
situations, ranging from a single specific
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anticipated alternative scenario to
multiple scenarios, including somewhat
less specific (but still nonetheless
bounded) scenarios. In all situations,
however, the contemplated changes
must be described in the permit
application in sufficient detail for the
relevant emissions units such that the
permitting authority can determine
whether all applicable requirements
have been identified and can craft
appropriate terms and conditions to
assure compliance with such
requirements. Where differing
applicable requirements would apply to
a particular emissions unit, depending
upon the nature and extent of the
change made, the permit should contain
alternative terms and conditions as
needed to assure compliance with all
applicable requirements under each
AOS which is reasonably anticipated to
occur.
If the permitting authority approves
the proposed AOSs for a particular
emissions unit, it will include in the
title V permit a description of the
anticipated changes associated with
each approved AOS, and for each AOS
will include associated applicable
requirements and terms and conditions
that assure compliance with each
identified applicable requirement, as
well as terms and conditions that assure
compliance with the related part 70
requirements relevant to the AOSs.
Alternative operating scenarios may
vary in their complexity. At one extreme
is a simple situation where a source
seeks approval for operating scenarios
that involve a very specific type and
number of changes to the defined
baseline operations of the relevant
emissions unit(s) (i.e., the changes can
be described exactly). An example of
this situation is the combustion of
various fuels in a boiler capable of
burning different fuels (where
combustion of each type of fuel is
subject to different SIP requirements).
See Example 1 discussed below.
A more complex situation involves
sources seeking approval for AOSs
encompassing a wider spectrum of
reasonably anticipated changes. Sources
here may not be able to determine
precisely in advance (i.e., at the time of
permitting) which of the changes and
implicated AOSs will be implemented
for the relevant emissions unit(s).
Depending on future market behavior,
the source eventually may implement
all or only some of these changes.
The type of detail needed to describe
an AOS and the changes anticipated to
occur under it can vary. Certainly the
need for greater detail is dependent
upon what is required to determine the
applicable requirements implicated by
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the anticipated changes. In many cases,
the number of applicable requirements
for anticipated changes can be reduced,
without loss of flexibility, through
strategic use of boundary conditions on
the AOS. Boundary conditions help to
define the relevant applicable
requirements implicated by authorized
physical or operational changes, which,
in turn, enables the permitting authority
to assure that all applicable
requirements and requirements of part
70 are contained in the permit when
designing AOSs.25 For example,
operational restrictions (such as those
on the type or amount of materials
combusted, processed, or stored) can be
used to delineate the scope of the AOS
by limiting which applicable
requirements apply under them.
The approaches approved to assure
compliance with applicable
requirements can also affect the
implementation of anticipated AOSs
and, therefore, indirectly affect the
changes approved under them. That is,
authorized changes must not adversely
impact the effectiveness of the control
devices or monitoring approaches
required by an AOS approved in the
permit. For example, changes involving
substances which are not effectively
controlled by the control device
required in the permit could not be
approved. This would also be true for
physical or operational changes which
would render inaccurate the monitoring
procedures approved in the permit for
assuring compliance with an applicable
requirement (e.g., PTE limit).
Compliance assurance terms for AOSs
and advance approvals can be greatly
simplified where the applicable
requirements can be streamlined (i.e.,
the compliance terms are based on the
most stringent requirement applicable to
the proposed changes and are effective
upon permit issuance). In guidance
generally referred to as ‘‘White Paper
Number 2,’’ we interpreted our part 70
rules to allow sources to streamline
multiple applicable requirements that
apply to the same emissions unit(s) into
a single set of requirements that assure
compliance with all the subsumed
25 Boundary conditions can also be used to
restrict the scope of advance approvals. The pilots
primarily used boundary conditions for this
purpose. Such conditions typically involved
restrictions that prevented certain different
applicable requirements from applying to the
changes otherwise authorized under minor NSR.
For example, a source owner opted to avoid the
applicability of major NSR by accepting an
emissions limit that restricts the PTE of the source
to below the threshold at which that requirement
would apply, or, in the case of an existing major
stationary source, a PAL that designates an
emissions limit below which major NSR would not
apply to changes made at the source.
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applicable requirements.26 If all the
applicable requirements that apply to a
set of changes are streamlined in the
permit and the permitting authority
approves the proposed streamlining, the
source need only comply with the
streamlined requirement. This benefits
all parties by simplifying and focusing
the compliance requirements contained
in the permit.
It should be noted that changing to an
AOS cannot be used to circumvent
applicable requirements or to avoid an
enforcement action. A switch to an AOS
does not affect the compliance
obligations applicable to a source under
its previous operations.
B. What information is necessary in a
title V permit application to seek
approval of an AOS?
Because the application forms the
basis for the content of the title V
permit, the discussion below is relevant
to the content of a permit that
authorizes AOSs. This section clarifies
the requirements for a complete
application and discusses minor
proposed revisions to these
requirements.
The provisions of 40 CFR 70.5(c)
contain the information that must be
submitted in a complete title V permit
application, including information
concerning proposed AOSs.27 We are
proposing minor revisions to 40 CFR
70.5(c) to clarify how certain aspects of
the requirements in that section should
be addressed when a source applies for
approval of AOSs.
Under the provisions of 40 CFR
70.5(c), the source generally must
describe the emissions of all regulated
air pollutants (as defined at 40 CFR
70.2) from any emissions unit, identify
all applicable requirements that apply to
each emissions unit, and describe how
it will meet these applicable
requirements. The source must provide
this information for existing operations
26 As explained in White Paper Number 2,
sources that seek to streamline applicable
requirements should submit their request as part of
their title V permit application, identifying the
proposed streamlined requirements and providing a
demonstration that the streamlined requirements
assure compliance with all the underlying,
subsumed applicable requirements. Upon approval
of the streamlined requirements, the permitting
authority would place the requirements in the title
V permit. See ‘‘White Paper Number 2 for Improved
Implementation of the Part 70 Operating Permits
Program,’’ March, 5, 1996, for the complete
guidance on the streamlining of applicable
requirements (https://www.epa.gov/ttn/oarpg/t5/
memoranda/wtppr-2.pdf). Where the source wishes
to streamline the advance approval under NSR with
all other relevant applicable requirements, the same
title V permit application can address both actions.
27 For the complete text of the elements that must
be included in a title V application, see 40 CFR
70.5(c).
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(i.e., baseline operations) and for any
reasonably anticipated changes for
which an AOS is proposed. The
description of AOSs in title V permit
applications may vary depending on the
situation (as previously discussed).
However, in every case the level of
detail in the description must be
sufficient for the permitting authority to
write permit terms and conditions that
assure compliance with all applicable
requirements and the requirements of
part 70 that will apply to the proposed
AOS. See 40 CFR 70.5(c)(3)–(7); 40 CFR
70.6(a)(9)(iii). If the source adequately
describes proposed AOSs in the part 70
permit application and the permitting
authority includes them in the permit
consistent with 40 CFR 70.6, the source
may subsequently implement the
physical and operational changes under
protection of the permit shield (where
available and granted by the permitting
authority) without triggering the permit
modification provisions of 40 CFR 70.7.
Similarly, the source must meet the
provisions of 40 CFR 70.5(c) concerning
advance approvals which are to be
incorporated into the title V permit.
Where a change is authorized in an NSR
permit and the permit contains terms
which would be effective upon issuance
of the title V permit and would assure
compliance with all applicable
requirements, then a straightforward
incorporation of the terms of the NSR
permit into the title V permit is all that
is necessary. However, where the NSR
advance approval terms would be
effective upon title V permit issuance
but would not address some other
requirement(s) that will apply to the
NSR-authorized changes (e.g., a MACT
standard), then additional information
about the changes relative to these other
requirements must be provided to the
permitting authority in the part 70
application. The permitting authority
would then develop permit terms
sufficient to assure compliance with all
requirements applicable to the NSRapproved changes as part of the title V
permit issuance, modification, or
renewal process. Use of a streamlined
limit is one acceptable approach when
requested by the source (see footnote 26
and example 3 below).
We are proposing to revise 40 CFR
70.5(c)(2) and (7) to use the term ‘‘AOS’’
in the interest of consistent terminology.
Existing 40 CFR 70.5(c)(2) uses the term
‘‘alternate scenario,’’ while existing 40
CFR 70.5(c)(7) uses ‘‘alternative
operating scenario.’’ We believe that
revising these paragraphs to use
consistent terminology, along with
proposing a definition for ‘‘AOS’’ and
conforming changes in other sections,
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will improve the clarity of the affected
paragraphs and reduce any confusion.
We are also proposing to revise 40
CFR 70.5(c)(3)(iii), (c)(7), and (c)(8) to
clarify our intent regarding the
information that must be included in an
application that proposes AOSs for
approval by the permitting authority.
The proposed revisions to each of these
sections are described below, along with
the rationale for proposing them.
The introductory text in 40 CFR
70.5(c) states generally that the
application must include information
for each emissions unit. Existing 40 CFR
70.5(c)(3)(iii) further requires that the
application provide the emissions rate
in tpy and in such terms as are
necessary to establish compliance
consistent with the applicable reference
test method. We are proposing to clarify
this regulatory requirement as it applies
to sources subject to title V permitting
requirements that employ an emissions
cap (e.g., PALs, PTE, Green Groups). In
particular, we are proposing that for the
operation of any emissions unit
authorized under an annual emissions
cap, a source can meet 40 CFR
70.5(c)(3)(iii) by reporting the aggregate
emissions associated with the cap. For
example, a source may take a plantwide
cap on its PTE so that it will not become
a major source for purposes of PSD,
thereby assuring that PSD will not apply
to any changes made at the source. For
purposes of the title V permit
application and this emissions cap, the
source need not provide individual tpy
figures for any new or modified
emissions units authorized under minor
NSR. Rather, emissions from such units
would be reported in the title V permit
application as part of the aggregate
emissions under the PTE cap.
Additional information may, however,
be required to describe the scope of any
changes authorized in minor NSR to
occur under any emissions cap or to
provide additional information relevant
to other requirements applicable to
these changes.
Under the proposed approach, an
emissions cap can act as a constraint on
annual emissions from each emissions
unit under the cap as well as on the
aggregated emissions from the group of
units. That is, in the extreme, a unit
could emit up to the full amount of the
cap if all other units under the cap had
zero emissions. Thus, for a group of
emissions units under an annual
emissions cap, the 40 CFR 70.5(c)(3)(iii)
requirement for unit-by-unit tpy figures
can be met by reporting in the permit
application that the emissions cap
represents the upper limit on emissions
both from each unit in the group and
from the entire group. This proposed
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52219
revision to 40 CFR 70.5(c)(3)(iii) simply
clarifies that in this particular situation,
more specificity is not needed.
Reporting emissions data in the above
proposed manner in the title V permit
application is permissible (including in
the case of a plantwide emissions cap),
except where the permitting authority
determines that more specific tpy
information is needed (e.g., where an
applicable requirement for a specific
emissions unit depends on the
emissions type or level).
We are proposing to revise 40 CFR
70.5(c)(7) in two ways. The existing
language in 40 CFR 70.5(c)(7) specifies
that the application must include
‘‘additional information as determined
to be necessary by the permitting
authority to define alternative operating
scenarios identified by the source
pursuant to 40 CFR 70.6(a)(9) of this
part or to define permit terms and
conditions implementing 40 CFR
70.4(b)(12) or 40 CFR 70.6(a)(10) of this
part.’’ First, we propose to modify the
existing language to clarify that the
permitting authority can require
additional information from the source
not only for adequately defining the
AOS, but also, as necessary, to craft
permit terms and conditions
implementing the proposed AOSs under
40 CFR 70.6(a)(9). We believe that this
proposed revision is implicit in the
existing language of 40 CFR 70.5 (e.g.,
40 CFR 70.5(c)(5)), but that a
clarification is appropriate.
Second, we propose to revise 40 CFR
70.5(c)(7) to clarify that the application
must include documentation
demonstrating that the source has
obtained all specific authorizations
required under the applicable
requirements relevant to any proposed
advance approvals or AOSs, or a
certification that the source has
submitted a complete application for
obtaining such authorizations. Based on
our pilot experience, we expect that
proposed advance approvals and certain
AOSs will involve one or more of the
following applicable requirements:
minor NSR, major NSR, and section
112(g) of the Act. These applicable
requirements all require permits or
other authorizations prior to
construction or modification of a
source.28 (In some cases, the overall
28 Some State, local, and Tribal air control
programs include ‘‘State-only’’ requirements (i.e.,
requirements not enforceable by EPA) that require
source owners or operators to obtain authorization
prior to construction. In instances where the
permitting authority elects to include such
requirements in the part 70 permit, there are
benefits to addressing them as part of a
comprehensive permit flexibility solution. These
requirements should, however, be labeled as ‘‘State-
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approach might be to avoid triggering
applicable requirements that require
additional authorizations, such as by
adopting a PAL or accepting a PTE
limit.)
It is important to stress that an AOS
merely incorporates authorizations
given under applicable requirements
and does not independently authorize
changes that are subject to review and
require specific approval. For this
reason, we are proposing the above
revision in the application
requirements, along with a related
revision to the AOS provisions of 40
CFR 70.6(a)(9), stating that the
permitting authority cannot approve an
AOS until all of the necessary
authorizations required under the
relevant applicable requirements have
been obtained. It is possible to process
the title V permit and, where needed, a
corresponding NSR permit
concurrently, but the title V permit
approving an AOS cannot be issued
before any necessary preconstruction
approval has been obtained.
Some applications for AOSs and
advance approvals may also contain
information needed to establish one or
more ‘‘approved replicable
methodologies’’ (ARMs). In section
VI.C.2.b of this preamble, we discuss
ARMs and their incorporation into part
70 permits. An ARM is an objective
protocol for determining values
pertaining to compliance or
applicability requirements, such as
temperature or emissions. Approved
replicable methodologies are permit
terms that are consistent with and
implement an applicable requirement or
requirement of part 70. A source that
wishes to have an ARM included in its
permit must provide sufficient
information in its application to define
the replicable methodology, its intended
function, the instructions for its use,
and the type of data required for its
implementation. See 40 CFR 70.5(c)(5)–
(c)(7). See section VI.C.2.b for more
information on ARMs.
Finally, we are proposing to revise 40
CFR 70.5(c)(8), which requires each part
70 permit application to include a
compliance plan. The existing
paragraph addresses applicable
requirements with which the source is
in compliance, applicable requirements
that will become effective during the
permit term (e.g., a newly promulgated
emission standard), and applicable
requirements with which the source is
only’’ consistent with 40 CFR 70.6(b)(2). Options for
flexible permit conditions to address State-only
applicable requirements potentially range widely,
depending on the State’s interpretation of its ability
to authorize changes in advance under these
requirements.
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not in compliance at the time of permit
issuance. We are proposing to revise
this section in two places to clarify that
such plans must address AOSs when
applications include them. This
proposal would add language to clarify
that, for applicable requirements
associated with an AOS, the compliance
plan must contain a statement that the
source will meet such requirements
upon implementation of the AOS or, if
a requirement becomes applicable after
implementation of the AOS, in a timely
manner. We believe that this revision
appropriately fills a gap in the existing
language. See proposed 40 CFR
70.5(c)(8)(ii)(D) and (iii)(D).
We solicit comment on whether the
proposed rule revisions noted above
provide sufficient clarity as to how the
application requirements of 40 CFR
70.5(c) are to be applied to sources that
seek approval of AOSs and/or
incorporation of advance approvals. We
also seek comment on whether the
proposed revisions are necessary or if
additional revisions are needed to
ensure that permit applications contain
sufficient detail to identify all
applicable requirements associated with
an AOS and/or advance approval. If you
believe that additional regulatory
revisions are needed, please identify the
proposed change and explain why it is
needed.
C. What terms and conditions must be
included in the title V permit for
approved AOSs?
Existing 40 CFR 70.6 details the
required content of a title V permit,
including the requirements for
reasonably anticipated operating
scenarios. In this section of the
preamble, we discuss how the existing
permit content requirements of 40 CFR
70.6 apply to AOSs and how the rule
revisions we are proposing are
consistent with this intent.
To standardize the terminology in 40
CFR 70.6, we are proposing to use the
term ‘‘alternative operating scenario’’ (or
its acronym ‘‘AOS’’) throughout 40 CFR
70.6(a)(9) as we have done in the other
sections of the rule. The proposed
revisions to 40 CFR 70.6(a)(9) also
clarify that the title V permit must
contain terms and conditions to
describe the AOSs, to assure compliance
with the applicable requirements
implicated by the AOSs, and to assure
compliance with the requirements of
part 70. Finally, as explained below, we
are proposing to modify 40 CFR
70.6(a)(1) to clarify that ARMs are one
type of operational requirement or
limitation that assures compliance with
applicable requirements. These items
are discussed below.
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As previously mentioned, no AOS is
needed where the changes would occur
under an advance approval contained in
an authorizing permit whose terms are
incorporated in the part 70 permit, as
well as any other applicable
requirements which would apply to the
advance approved changes, and those
terms are effective upon issuance of the
part 70 permit. For example, our pilot
experience suggests that no additional
flexibility provisions may be needed in
a title V permit beyond the
incorporation of NSR permit terms
establishing an advance approval under
minor NSR and a PAL or PTE limit that
prevents the applicability of major
NSR.29 On the other hand, AOSs can be
particularly useful either where: (1) A
new or existing unit with frequently
changing operations would be subject to
certain emissions standards in different
ways depending on the type of materials
used, rate of production, and type and/
or amount of product produced; or (2)
an existing unit would be subject to an
applicable requirement associated with
an advance approved change only upon
implementation of the authorized
change.
1. Terms and Conditions To Describe
Approved AOSs
If the permitting authority approves
an AOS, the permit must include a
description of the baseline operating
scenario for each included emissions
unit, the authorized physical or
operational changes included in each
AOS, and the applicable requirements
that apply under each scenario
(including those requirements newly
applying or not applying as a result of
the authorized changes). Expectations
for AOS descriptions in the permit are
similar to those previously identified for
AOS descriptions in complete
applications. As mentioned previously,
the type of detail in such descriptions
and the need for one or more boundary
conditions can vary depending on the
nature of the change and the applicable
requirements implicated by the changes.
A permit with an AOS for a particular
emissions unit normally would include
a description of the unit operating in its
baseline mode of operation. For each
approved AOS, the physical and
operational changes which have been
authorized should then be identified
relative to this baseline operation. In all
cases, the description of each AOS must
be adequate to link the triggered
29 As needed, additional terms would be added to
assure compliance with applicable requirements
beyond NSR that are implicated by the advance
approved changes.
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applicable requirements to the terms
which assure compliance with them.
We are proposing revisions to 40 CFR
70.6(a)(9) to clarify what constitutes an
acceptable description for an AOS (see
proposed revision to 40 CFR
70.6(a)(9)(iii)). We are also proposing a
revision to 40 CFR 70.6(a)(9)(iii) to make
clear that the permitting authority
cannot approve an AOS until all of the
necessary authorizations relevant to the
applicable requirements have been
obtained, that is, until the source has
been approved to proceed by the
permitting authority where such prior
authorization is required (e.g., approvals
under major and minor NSR and section
112(g) of the Act).30 Finally, as
mentioned, where a source is unable to
predict, at the time of permit issuance,
which of several reasonably anticipated
changes it actually will make, it can
seek approval for a range of changes and
applicable requirement combinations at
a particular emissions unit by including
multiple AOSs.
2. Terms and Conditions To Assure
Compliance With Applicable
Requirements
In this section, we discuss our
proposal related to permit content to
assure compliance with all applicable
requirements.
jlentini on PROD1PC65 with PROPOSALS2
a. Proposed Clarifications to the AOS
Provisions
The provisions of 40 CFR
70.6(a)(9)(iii) require that, for each AOS
for an emissions unit, the permit must
contain terms and conditions to assure
compliance with all the applicable
requirements that apply to the
emissions units operating in that AOS.
This means that the permit must
include, for each relevant emissions
unit, the applicable emissions limits,
compliance approaches, and
monitoring, recordkeeping, reporting,
and testing (MRRT) requirements as
required by the applicable requirements
as well as those required otherwise
under 40 CFR 70.6(a)(3) (e.g., periodic
monitoring) for the compliance
approaches. In addition, the permit
must incorporate all advance approvals,
such as those authorized under NSR, as
well as the description of changes
authorized in each AOS as described
above. For a permit containing more
than one AOS for an emissions unit, the
permit must contain a clear description
of each one so that there is no confusion
with respect to which AOS is
implicated at any given time.
30 See
footnote 22.
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b. Proposed Revisions for ARMs
As stated, title V permits are required
to assure compliance with all applicable
requirements. Sometimes, changes
occur at a source that may cause the
need to recalculate/update a value used
either in determining compliance of the
source with an applicable requirement
or in determining the applicability of a
requirement. An advance approval or an
AOS can incorporate flexibility in a
permit, but the scope of changes that
can be authorized in them can be
severely limited with respect to a
particular applicable requirement, if the
changes require case-by-case review/
approval procedures and possible
permit revision in order to ensure
ongoing compliance with all applicable
requirements. To facilitate
implementation of advance approvals
and AOSs, and to encourage other
permitting techniques that reduce in
general the need for permit
modifications (in a manner consistent
with part 70), we are proposing the use
of an ARM that has been approved by
a permitting authority and incorporated
into a title V permit.
In particular, we are proposing to
define ‘‘approved replicable
methodology’’ or ‘‘ARM’’ at 40 CFR 70.2
as title V permit terms that: (1) Specify
a protocol which is consistent with and
implements an applicable requirement
or requirement of part 70, such that the
protocol is based on sound scientific/
mathematical principles and provides
reproducible results using the same
inputs; and (2) require the results of that
protocol to be used for assuring
compliance with such applicable
requirement or requirement of part 70,
including where an ARM is used for
determining applicability of a specific
requirement to a particular change.
Within the scope of this definition, an
ARM may be used to assure that a given
requirement does not apply in a
particular situation.
The terms of an ARM must specify
when the ARM is to be used, the
applicable methodology (e.g., equation
or algorithm) and the purpose for which
the output obtained upon the execution
of the prescribed methodology will be
used (e.g., to determine compliance
with an applicable requirement or to
modify the level of the parameters used
to determine compliance in the future).
All necessary terms and conditions
must be included in the permit at the
time the ARM is approved so that no
permit revision will be required in the
future to implement the ARM.
It is important to emphasize that an
ARM, like any provision of a part 70
permit, cannot modify, supersede, or
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52221
replace an applicable requirement,
including, but not limited to, any
monitoring, recordkeeping, or reporting
required under applicable
requirements.31 Instead, ARMs are a
strategic approach for incorporating into
a title V permit relevant applicable
requirements and the requirements of
part 70. The ARM provides a method for
obtaining and updating information
consistent with the intent of applicable
requirement(s) or requirement(s) of part
70 in such a manner so as to avoid the
need to reopen or revise the permit to
incorporate the updated information. As
such, an ARM must work within and be
consistent with the applicable part 70
rules that govern permit revisions.
The protocol to obtain information
under an ARM must be objective and
scientifically valid and reliable—such as
an EPA test method or monitoring
method (usually specified in the
applicable requirement itself.) Note that
an ARM also includes the instructions
governing how the results of the
protocol are to be used. For example, an
ARM could specify that firebox
temperature measurements taken during
a performance test of a thermal oxidizer
be used to revise a previously imposed
minimum firebox operating temperature
of the oxidizer.
We believe that ARMs are authorized
under title V of the Act and its
implementing regulations. Section 502
sets forth the minimum elements for a
State operating permit program. Among
other things, section 502 provides that
for a State operating permit program to
be approved, the permitting authority
must have adequate authority to ‘‘issue
permits and assure compliance by all
sources required to have a permit * * *
with each applicable standard,
regulation or requirement’’ under the
Act. See CAA section 502(b)(5)(A).
Section 504(a) of the Act also requires
that each title V permit contain
‘‘enforceable limitations and standards
* * * and such other conditions as are
necessary to assure compliance with
applicable requirements of this Act,
including the requirements of the
applicable implementation plan.’’ The
Act further provides that any State
operating permit program must include
‘‘adequate, streamlined, and reasonable
procedures * * * for expeditious
review of permit actions.’’ See CAA
section 502(b)(6).
31 Under the authority of 40 CFR 70.6(a)(3),
however, the permit can also contain additional
streamlined monitoring or gap-filling periodic
monitoring as needed to assure compliance with
applicable requirements. An ARM can operate on
the information gathered under these obligations as
well.
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The part 70 regulations implement
these requirements. Section 70.4 sets
forth the required elements for a State
operating permit program. Such State
programs must provide for the issuance
of permits that contain appropriate
terms and conditions that assure
compliance with all applicable
requirements and the requirements of
part 70. See generally 40 CFR 70.4(3)(i)–
(ii), (v). The threshold requirement that
a part 70 permit contain terms and
conditions that assure compliance with
applicable requirements and the
requirements of part 70 is also reflected
in other parts of the part 70 regulations.
See, e.g., 40 CFR 70.5(c)(4)–(5),
70.6(a)(1)(i), 70.6(a)(9)(iii). For example,
40 CFR 70.6(a)(1) provides that the
permit include ‘‘those operational
requirements and limitations that assure
compliance with all applicable
requirements.’’ Section 70.6(a)(1)(i)
further provides that the permit shall
identify the origin and authority for
each term and condition. See 57 FR
32275 (‘‘Section 70.6(a)(1)(i) requires
that the permit reference the authority
for each term and condition of the
permit. Including in the permit legal
citations to the provisions of the Act is
critical in defining the scope of any
permit shield, since the permit shield, if
granted, extends to the provisions of the
Act included in the permit.’’). An ARM,
as proposed now, constitutes permit
terms designed to assure compliance
with applicable requirements or the
requirements of part 70 and accordingly
falls squarely within the authority of
title V and its implementing regulations.
In our pilot experience, we found that
some permitting authorities already use
part 70 permit terms (similar to ARMs)
that assure compliance with applicable
requirements or the requirements of part
70, are self-implementing, and avoid the
need for the source to seek multiple
permit revisions. Based on our
experience in the pilot program with
such permitting techniques and in an
effort to encourage efficient permitting
techniques, we propose to define an
ARM in the manner described above.
Under the proposed ARM definition,
an ARM may be used to implement an
applicable requirement. As an example
of one type of ARM, consider a source
subject to the MACT standard for Paper
and Other Web Coating (40 CFR part 63,
subpart JJJJ), which requires a 95
percent reduction in HAP emissions for
existing sources. Like many emission
standards, subpart JJJJ requires the
source to assess ongoing compliance
with the emissions limit by monitoring
an operating parameter of the air
pollution control device. Where a
source uses a thermal oxidizer to
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comply with the emissions limit, the
rule requires the source to conduct a
performance test to demonstrate initial
compliance and to demonstrate ongoing
compliance by continuously monitoring
the combustion temperature in the
combustion chamber of the oxidizer. To
establish the minimum combustion
temperature that will serve as the basis
for future compliance determinations,
subpart JJJJ requires the source to
monitor the combustion temperature
throughout the performance test, and to
calculate the average combustion
temperature achieved by the oxidizer
during the test. Provided that the
performance test demonstrated
compliance with subpart JJJJ, the
average combustion temperature
determined during the test is
established as the minimum
temperature limit for the oxidizer in the
permit. This value may change with
each successive performance test that
demonstrates compliance.32
A source subject to subpart JJJJ
proposes to use an ARM consistent with
this standard to accommodate
anticipated changes in the operating
parameter limit resulting from future
performance demonstrations without
requiring a permit revision. The ARM
would consist of the test methods and
procedures specified under subpart JJJJ
for demonstrating compliance and
determining the minimum oxidizer
temperature which indicates
compliance with the standard (as
described in the paragraph above). Upon
approval of the ARM into the permit,
the source would no longer be required
to revise the permit each time it
conducted a performance demonstration
to place the most recent temperature
value indicative of compliance on the
face of the permit. Instead, the permit
would require the source to: (1) Use the
ARM (i.e., the test methods and
procedures required under subpart JJJJ)
to determine the temperature value
indicative of compliance; (2) maintain
records of this temperature; and (3) use
this temperature for all compliance
monitoring and reporting purposes
dictated by subpart JJJJ, until and unless
the permittee implements the ARM
again. If the permitting authority for the
source requires regular performance
tests, the schedule for such tests also
could be included in the ARM.
The MACT General Provisions (40
CFR part 63, subpart A) also apply in
32 Although subpart JJJJ requires only an initial
performance test, many States require periodic
performance tests to verify that the control device
continues to achieve the emissions limit. Where
this is the case, the operating limit typically is
recalculated based on the temperature during each
test.
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part to sources subject to subpart JJJJ.
The General Provisions include the
following provisions related to
conducting performance tests:
Requirements for notifications; quality
assurance (including submission of a
site-specific test plan as requested by
the permitting authority); the test
method audit program; conduct of tests;
and data analysis, recordkeeping, and
reporting. The ARM does not abrogate
such procedural requirements, it simply
incorporates these requirements in the
permit.
A second type of ARM may be used
in a part 70 permit to ensure that a legal
limit requested voluntarily by the
source effectively constrains the
source’s PTE below a certain threshold
so as to avoid the applicability of certain
requirements. By complying with such
PTE limits, sources demonstrate on an
ongoing basis that they are not subject
to a requirement that would otherwise
be triggered at a particular emissions
threshold. Some PTE limits are
applicable requirements (e.g., if
imposed by a SIP program or as a
condition of an NSR permit). In
addition, part 70 operating permits can
be used as a legal mechanism for
establishing EPA and citizens’ authority
to enforce terms and conditions limiting
a source’s PTE. See 40 CFR 70.6(b)(1).
Permitting authorities have some
discretion in fashioning such terms and
conditions. We believe that the ARM
concept could be used to establish
effective PTE limits in agreement with
40 CFR 70.6(b)(1).33
As an example of how the ARM
concept can be used to assure
compliance with a PTE limit, consider
a source in the process of renewing its
title V permit that proposes to take a
PTE limit of 99 tpy on its VOC
emissions to avoid being classified as a
major VOC source. The PTE limit, once
approved and incorporated into the title
V permit, has the effect of exempting the
source from major NSR requirements
that only apply to existing major VOC
emitters. To assure compliance with the
99 tpy PTE limit, the source proposes a
quantification methodology to the
permitting authority by which the
source would determine total VOC
emissions on an ongoing basis.34 In this
33 We have proposed in the definition of ARM
that the otherwise qualifying replicable protocol be
consistent with and implement an applicable
requirement or requirement of part 70 (emphasis
added). Limits on PTE may be established pursuant
to part 70, and such a PTE limit would be a
requirement of part 70 and thus could be in part
implemented through an ARM.
34 In the above PTE example, assume that the
emissions determinations were based on emissions
factors derived from a stack test. If there is a
possibility that a subsequent stack test may be
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instance, the source will determine VOC
emissions with an equation that sums
all the individual VOC emissions from
each emissions unit. Provided that this
methodology relies on objective,
repeatable protocols (i.e., the method of
calculating the individual units’ VOC
emissions is clear) it can become an
ARM when approved by the permitting
authority and included in the title V
permit. The ARM would include
requirements governing when the
procedures were to be used and how the
values to be input into the equation
would be determined.
We found permit terms, similar to
ARMs, to be useful in maintaining the
effect of the advance approvals found in
the flexible permit pilots. Two of the
pilot permits contained replicable
testing procedures. These procedures,
once implemented, determined the
control device operating parameter
values that the source must monitor to
demonstrate compliance with capture
and destruction efficiency requirements
(i.e., the applicable requirement).
Without the replicable testing
procedures in the permit, those values
would have been included on the face
of the permit, and the source would
have had to seek a permit revision each
time it repeated the testing procedures
and the operating parameter values
changed.35 Another pilot permit
specified the process by which an
emissions factor could be updated and
used to determine whether the source’s
emissions remained under a PTE cap.
By including this process (replicable
testing and/or emissions factor updating
procedures) in the permit instead of
specific operating values and emissions
factors, the source could update those
values and indicate compliance based
on the latest results consistent with the
replicable testing procedures in the title
V permit, and forego a permit revision
each time the values change.
In addition to proposing a definition
of an ARM, we also propose modifying
40 CFR 70.6(a)(1) to include a reference
to ARMs, because ARMs are an example
performed, which would require revision of those
emissions factors in the near future, the source or
permitting authority may consider including in the
permit an ARM. The ARM could direct the source
to use emissions factors derived from the most
recent stack test, rather than listing specific factors
in the PTE equation contained in the permit,
eliminating the need for a permit revision once new
factors are established.
35 Although an ARM can reduce the number of
permit revisions a source must make, it cannot
modify an applicable requirement. For example,
there are some instances where the applicable
requirement requires a notice to the permitting
authority, such as where the requirement calls for
notice of a performance test or the submission of
certain performance test results. An ARM does not
abrogate these requirements.
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of permit terms that assure compliance
with applicable requirements. Although
we do not believe that the proposed
regulatory change to 40 CFR 70.6(a)(1) is
needed, given that all permits must
include terms that assure compliance
with applicable requirements and the
requirements of part 70, we are
proposing the change to promote clarity.
We recognize that we could modify
other provisions of part 70, such as 40
CFR 70.6(a)(9),36 to include a reference
to ARMs, but given the structure and
content of the existing regulations, we
do not believe such additional changes
are needed. We solicit comment,
however, on whether additional
regulatory changes would be useful to
encourage the use of this efficient
permitting technique.
3. Terms and Conditions To Assure
Compliance With Other Part 70
Requirements
In addition to the terms and
conditions to assure compliance with all
applicable requirements, the permit
must contain terms and conditions that
assure compliance with the
requirements of part 70. Section
70.6(a)(9)(i) currently requires ‘‘the
source, contemporaneously with making
a change from one [AOS] to another, to
record in a log at the permitted facility
a record of the [AOS] under which it is
operating.’’ We are proposing to clarify
this provision to identify more clearly
the information that must be included
in the log and when the log must be
updated.
Overall, we expect that the log will be
clear and complete in its description of
which AOS and associated permit terms
and conditions are being implemented.
Specifically, we propose that the source
be required to maintain an on-site log
that includes, for each time an AOS is
implemented at the source: the
operational or physical change which
causes the shift to the AOS, the
emissions unit included under the
scenario, a reference to the applicable
requirement(s) (including those newly
applicable to the emissions unit as a
result of the change), a reference to the
applicable permit terms and conditions
which apply to the AOS and are
implemented by the source, and the
dates when the source operated under
the AOS (see proposed 40 CFR
70.6(a)(9)(i)).37, 38 A source can cross36 In pertinent part, 40 CFR 70.6(a)(9) provides
that for an AOS, the part 70 permit must contain
appropriate terms and conditions to ensure that ‘‘all
applicable requirement and the requirements of this
part’’ are met. An ARM constitutes an example of
such permit terms.
37 Certain applicable requirements require that
additional information be included in an on-site
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52223
reference the permit in providing the
information required for the log, but the
cross-reference must be clear and
specific and all of the information
required for the log must be identified,
including, but not limited to, the
identity of the AOS implemented and if
alternative terms and conditions are
provided for such AOS, which terms
and conditions were actually
implemented by the source.
We are seeking comment on whether
our proposed revisions to 40 CFR
70.6(a)(9)(i) appropriately clarify the
required content of the on-site log of
AOSs operated at the source. We also
seek comment on whether we have
achieved the proper balance between
the need for information and the need
to minimize administrative burden in
proposing that log entries be required
only when a source adopts a different
AOS. Is the proposed log content
adequate to determine which AOS is
being implemented by the source?
Existing 40 CFR 70.6(a)(9)(ii) states
that the title V permit may extend the
permit shield described in 40 CFR
70.6(f) to all terms and conditions under
each AOS. We are not proposing to
change this paragraph, other than to
adopt the term ‘‘AOS’’ for consistency.
Thus, the permit shield, where provided
for by the permitting authority, may be
extended to the terms and conditions of
ARMs and AOSs, provided they have
been the subject of notice and comment.
See 57 FR at 32277 (July 21, 1992); see
also 40 CFR 70.7(e)(2)(vi). The contents
of the on-site implementation log, such
as its description of requirements which
apply to a particular AOS, are not
permit provisions for purposes of the
permit shield. Thus, a source will not be
deemed to be in compliance with
applicable requirements of the Act
simply because it is in compliance with
the description of applicable
requirements contained in the log (if the
description is inaccurate). Similarly, a
source owner or operator who
log. These data can be combined with that which
would be required under the proposed part 70
revisions. For example, the Pharmaceuticals
Production MACT standard (40 CFR part 63,
subpart GGG) requires the source to log
considerably more information about its ‘‘operating
scenario.’’ See 40 CFR 63.1259(b)(8) and the
definition of ‘‘operating scenario’’ at 40 CFR
63.1251.
38 A source, however, would not need to log a
change to an emissions unit unless an AOS is
implicated by the change, or a source stops
operating under an AOS and returns to baseline
operating conditions as a result of the change. In
particular, no log entry is needed for a source
making a change where the change has been
advance approved under minor NSR, the title V
permit contains the advance approval, and these
terms are in effect upon issuance of the title V
permit (i.e., no AOS is involved).
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incorrectly applies the procedures and
criteria for an ARM contained in the
permit will be considered not to be in
compliance with the terms of the permit
(and therefore not in compliance with
the Act).
Finally, we would like to clarify our
expectations for how monitoring
relative to AOS implementation is to be
included in the semi-annual monitoring
reports required by 40 CFR
70.6(a)(3)(iii)(A). In general, the semiannual reports must identify the AOS(s)
implemented during the 6-month period
and include monitoring information
relating to such AOS(s). Such
monitoring information provides
permitting authorities important
information on source operations. The
information also helps inform the
permitting authority as to the frequency
and duration of the AOSs actually
implemented.
In addition, the semi-annual
monitoring reports must identify any
ARMs implemented in the 6-month
period. For ARMs that generate values
related to parametric monitoring (e.g.,
an ARM used to determine the new
value of a control device operating limit
after a performance test, or an ARM
used to determine compliance with a
PTE limit), the source must also include
the results of the ARM used during the
6-month period in the semi-annual
report. The report will, therefore,
summarize the monitoring data
referenced to the emissions unit,
emissions limit, and ARM output.
jlentini on PROD1PC65 with PROPOSALS2
D. What are some examples of how
AOSs and advance approvals can be
used to provide operational flexibility?
In this section, we present two
examples to illustrate how to apply the
requirements of 40 CFR 70.5(c) and
70.6(a)(9) to AOSs. The first example is
for an AOS that involves the use of an
existing boiler with dual fuel capability.
The second example uses a combination
of advance approvals and AOSs to add
solvent storage tanks over the term of a
source’s title V permit.
Example 1: Boiler With Dual Fuel
capability
This is a simple example of an AOS,
and the application and permitting
requirements are quite straightforward.
The relevant emissions unit is an
existing boiler that is authorized for and
capable of burning either distillate fuel
oil or natural gas. The boiler is part of
a major stationary source subject to the
title V permitting requirements. The
boiler is subject to a pre-existing minor
NSR permit which authorized its
construction and limited its subsequent
total emissions, and to different SIP
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emissions limits (and associated MRRT
requirements) depending on which fuel
is in use. The minor NSR permit
remains in effect. The source reasonably
anticipates that it may wish to switch
fuels during the term of its title V
permit, and proposes to the permitting
authority to designate combustion of
natural gas as the baseline operating
scenario and address the combustion of
distillate fuel oil as an AOS.
In this example, the minor NSR
permit terms (previously used to
authorize construction of the boiler), the
applicable SIP emissions limits, and the
associated MRRT requirements are the
only applicable requirements. The
boiler is not subject to any of the NSPS
for ‘‘steam generating units’’ (i.e.,
boilers) because of its size and date of
construction. That is, it is below the size
cutoff for the NSPS that were in effect
when it was built (40 CFR part 60,
subparts D, Da, and Db), and it was built
prior to the cutoff date for the NSPS that
does cover boilers of its size (subpart
Dc). By virtue of its construction date,
size, and fuel, the boiler is classified as
an existing large liquid fuel unit under
the MACT standard for Industrial,
Commercial, and Institutional Boilers
and Process Heaters (40 CFR part 63,
subpart DDDDD). As such, the only
applicable requirement under the
MACT standard is to submit an ‘‘initial
notification’’ to the permitting authority,
which the source has already done.
When distillate oil is fired, the boiler
is subject to limits of 10 percent opacity
and 1 percent sulfur in the fuel. No such
restrictions apply when natural gas is
being fired. Different SIP emissions
limits also apply to emissions of
particulate matter, nitrogen oxides, and
carbon monoxide for each fuel. This
existing unit was constructed under a
minor NSR permit, but switching
between the fuels will not trigger minor
or major NSR, an NSPS, or the MACT
standard because the boiler was
designed to accommodate both fuels,
and it has historically been authorized
to use both fuels in its State operating
permits. Thus, the anticipated fuel
switches are operational changes that
trigger only different SIP requirements.
The design of the burners in the
boiler, coupled with proper operation
and maintenance, is sufficient to meet
the SIP limits for both fuels for
particulate matter, nitrogen oxides, and
carbon monoxide, as well as opacity
when distillate oil is fired (based on
performance tests). To meet the percent
fuel sulfur requirement for distillate oil
firing, the source will purchase fuel at
or below 1 percent sulfur. In addition,
under the terms of its existing (and still
effective) minor NSR permit, the source
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will have to provide periodic analyses
of the percent sulfur in the fuel, as well
as whenever the source changes fuel
suppliers.
To establish the AOS, the permit
would identify and describe the AOS, in
this case combustion of distillate oil,
and identify all applicable requirements
which apply when distillate oil is
combusted. The permit must also
include terms and conditions that
assure compliance with all applicable
requirements (as required under
proposed 40 CFR 70.6(a)(9)(iii)), and
include a requirement for the source to
keep a contemporaneous log that
records the information required by
proposed 40 CFR 70.6(a)(9)(i),
including, but not limited to: the
affected emissions unit (i.e., the boiler),
a reference to the applicable
requirements applying to the boiler
when burning distillate oil, a reference
to the applicable permit terms which
assure compliance with these
requirements, and the dates the source
began and ceased combustion of
distillate oil. Since the MRRT applicable
requirements detail all the relevant
compliance procedures, there is no need
for additional permit information to be
contained or cross-referenced into the
log for this purpose.
The title V permit for the source also
must require the source to submit a
semi-annual monitoring report. See 40
CFR 70.6(a)(3)(iii)(A). In this example,
once the facility implements the AOS
(i.e., begins combusting distillate fuel
oil), the next monitoring report would
identify, for the relevant time periods,
the AOS implemented and provide
monitoring information relative to that
AOS. The report would also contain
monitoring information for the baseline
natural gas combustion operations, if
the source operated both in the baseline
mode and under the AOS during the 6month reporting period.
Example 2: Future Addition of Volatile
Organic Liquid (VOL) Storage Tanks
A synthetic organic chemical
manufacturing facility located in an
ozone attainment area seeks a title V
permit renewal and intends to add VOL
storage tanks to an existing tank farm
and store various VOLs at different
times in the new and existing tanks over
the term of its renewed permit. The
source will have to obtain all necessary
advance approvals in a minor NSR
permit for construction of the new
tanks. In addition, the source will apply
for AOSs in its title V permit to address
future operating scenarios involving
storing different VOLs at different times
in the new tanks and also its existing
tanks (since these scenarios will
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implicate different applicable
requirements)
Advance Approvals
In this example, the source applied
for advance approvals under NSR to
authorize the construction of up to 10
new VOL storage tanks of up to 30,000
gallons in capacity. Because the source
operates under a VOC PAL, the new
tanks will not trigger major NSR for
VOC. In its minor NSR permit
application, the source proposed to the
permitting authority that this emissions
cap, by limiting aggregate VOC
emissions (including those from the
new tanks), would also satisfy the
requirements of minor NSR related to
the protection of the NAAQS and PSD
increments.39 Although the source does
not know precisely the sizes or number
of the new tanks or the materials to be
stored in them, it acknowledged in its
minor NSR permit application that the
requirements of the NSPS for Volatile
Organic Liquid Storage Vessels (40 CFR
part 60, subpart Kb) would apply to
each new tank. In addition, the source
stated that it would use a submerged fill
pipe for tanks with capacity of 2,000
gallons or more which is the SIP
requirement for such tanks when they
otherwise are not required to be
controlled to comply with subpart Kb.
The source did not address any other
SIP requirements for VOL storage tanks
in its application because these
requirements do not apply to tanks with
capacity below 40,000 gallons, and the
source is not seeking approval for any
new tanks over 30,000 gallons in
capacity. In addition, although it is
subject to the MACT standard for the
Synthetic Organic Chemical
Manufacturing Industry (typically
referred to as the ‘‘Hazardous Organic
NESHAP’’ or the ‘‘HON,’’ 40 CFR part
63, subpart G), the source did not
address the requirements of this
standard in its minor NSR application
because the State in which this example
source is located implements MACT
52225
standards through its title V permit
program (see below) rather than in the
context of its minor NSR program.40
The control requirements of subpart
Kb vary with the size of the storage tank
and the maximum true vapor pressure
of the stored liquid. An advance
approval must describe the changes that
the source may implement, which in
this example consist of the reasonably
anticipated combinations of new tank
size and stored liquid vapor pressure,
along with the requirements (i.e.,
subpart Kb and SIP provisions) that
would apply for each. One way to do so
would be to use a table such as Table
VI–1 below, which uses metric units to
match the metric units used in subpart
Kb. Note that because the source in this
example sought advance approval only
for new tanks up to 30,000 gallons (114
cubic meters (m3)) in capacity, the table
addresses only tanks up to this size even
though subpart Kb contains provisions
specific to larger tanks.
TABLE VI–1.—ADVANCE APPROVALS FOR NEW TANKS a
Tank size, V (m3)
Stored liquid maximum true vapor
pressure, VP (kPa)
Emissions limitation from 40 CFR
part 60, subpart Kb
MRRT citations from 40 CFR part
60, subpart Kb
V < 75 ............................................
75 ≤ V ≤ 114 ..................................
75 ≤ V ≤ 114 ..................................
Any ................................................
VP < 15.0 ......................................
15.0 ≤ VP < 27.6 ..........................
75 ≤ V ≤ 114 ..................................
27.6 ≤ VP < 76.6 ..........................
Not applicable.
Not applicable.
§§ 60.116b(a)–(e).
§ 60.113b(a),
§ 60.115b(a),
§§ 60.116b(a)–(c), (e).
§ 60.113b(b),
§ 60.115b(b),
§§ 60.116b(a)–(c), (e).
§ 60.113b(c) or (d), § 60.115b(c)
or (d), §§ 60.116b(a), (b), (e).
75 ≤ V ≤ 114 ..................................
76.6 ≤ VP ......................................
Not applicable ...............................
Not applicable ...............................
None .............................................
§ 60.112b(a)(1) Fixed roof w/internal floating roof; or
§ 60.112b(a)(2) External floating
roof; or
§ 60.112b(a)(3) Closed vent system and control device ≥ 95%
efficient.
§ 60.112b(b) Closed vent system
and control device ≥ 95% efficient.
§ 60.113b(c) or (d), § 60.115b(c)
or (d), §§ 60.116b(a), (b), (e).
jlentini on PROD1PC65 with PROPOSALS2
a The source is authorized to add up to 10 new tanks, each of which is covered by the scope of Table IV–1. A permanent submerged fill pipe
is required for any of the 10 advance approved tanks with capacity ≥7.6 m 3 that is not controlled with an internal floating roof, external floating
roof, or closed vent system and 95%-efficient control device.
In this example, the permitting
authority granted advance approval in a
minor NSR permit for the source to
construct tanks meeting each of the
conditions described in Table VI–1. The
permitting authority determined that no
further restrictions on the proposed
tanks other than SIP and subpart Kb
compliance and the major NSR PAL for
VOC emissions would be necessary in
the minor NSR permit, because the
maximum number of proposed new
tanks could be accommodated within
the source’s VOC PAL (due to pollution
prevention (P2) initiatives undertaken
by the source) and would not cause
concern with NAAQS or PSD increment
protection or Class I area impacts. In
this case, the permitting authority chose
to incorporate Table VI–1 directly into
the minor NSR permit to identify the
requirements which apply to the new
tanks, regardless of size, type, and/or
number.
39 Under the provisions of parts 51 and 52, a
major NSR PAL does not inherently affect the
applicability of minor NSR. Some State minor NSR
rules may vary on this point, but for purposes of
this example we assume that minor NSR continues
to apply beneath the major NSR PAL.
40 The acronym ‘‘NESHAP’’ stands for National
Emission Standards for Hazardous Air Pollutants.
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Title V Renewal With AOSs
The source’s title V renewal
application would identify both the
existing emissions units (i.e., the units
currently comprising the tank farm) and
the new tanks authorized under the
minor NSR permit advance approval,
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and would contain any AOSs that the
source wants to propose. The title V
application must identify all applicable
requirements that are implicated by
each proposed AOS.
The source has opted to make the
universe of requirements potentially
applicable to the advance approved new
tanks more manageable by accepting a
boundary condition, specifically a
maximum tank volume of 30,000
gallons (114 m 3). This condition does
not restrict the source’s flexibility, since
only tanks at or below the 30,000 gallon
threshold are anticipated to be
constructed, but it does have the effect
The NESHAP promulgated in 40 CFR part 63 are
typically referred to as MACT standards.
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of precluding the applicability of the
NSPS requirements that would apply to
tanks above that size.41 The source also
has committed to store only materials
with maximum true vapor pressure of
less than 15 pounds per square inch
(psi) (103 kilopascals (kPa)). This ceiling
on vapor pressure does not affect the
applicability of control requirements,
but is necessary for calculating
maximum theoretical emissions from
the new tanks and assessing the ability
of existing add-on control devices to
accommodate any increased emissions.
The existing tanks are all currently
within these boundary conditions. The
source wishes to retain the option to
store materials that contain HAPs in all
of the tanks, which could implicate the
requirements for storage vessels in the
HON. In this example, the facility was
originally constructed in the late 1980’s,
so the existing tanks are subject to the
requirements of subpart Kb, and the
source is considered an existing
‘‘affected source’’ for purposes of the
HON. The applicable requirements to be
listed in the renewal application for the
new and existing tanks include the SIP
emissions limitations, the requirements
of subpart Kb, the requirements of the
minor NSR permit (which are identical
to the requirements of the SIP and
subpart Kb as set out in the advance
approvals in Table VI–1), and the
requirements of the HON.
The source has conducted a
streamlining analysis of applicable
requirements related to the emissions
limitations for each tank.42 The source
provided supporting documentation in
its permit application for this
streamlining analysis, and the
permitting authority reviewed and
approved it. The analysis shows that for
new and existing tanks that are storing
materials that do not contain HAPs,
compliance with the requirements of
subpart Kb also will satisfy the control
requirements of the SIP. For tanks not
storing HAPs, the SIP requirements are
the most stringent applicable
requirements only when subpart Kb
does not apply (i.e., when the tank size
and/or vapor pressure are below the
respective applicability limits for
subpart Kb).
For tanks that are storing materials
that contain HAPs and are subject to the
HON (i.e., capacity ≥ 38 m3), the HON
specifies that subpart Kb does not
apply.43 Tanks storing HAPs that are
below the size cutoff for HON
applicability are also below the
applicability cutoff for subpart Kb
(which is 75 m3); thus, at this facility
subpart Kb does not apply to new or
existing tanks that store materials
containing HAPs. The streamlining
analysis provided by the source and
approved by the permitting authority
shows that compliance with the
requirements of the HON will satisfy the
control requirements of the SIP for both
the new and existing tanks that store
HAP-containing materials. The SIP
requirements are most stringent only for
HAP-containing tanks that are below the
size and/or vapor pressure cutoffs for
control under the HON.
To maintain the flexibility to change
the material stored in each tank (an
operational change), the source
requested AOSs in its title V permit.
(The source does not expect to modify
the volume of any existing storage tanks,
or of any new tanks after they are
initially constructed, and therefore did
not request AOSs to address such
physical changes.) Each set of operating
conditions that implicates a different set
of applicable requirements would
require an AOS. The necessary AOSs
vary depending upon the capacity of a
given tank. For example, no AOSs are
needed for a new or existing storage
tank that has a capacity of less than 7.6
m3 because no requirements apply
regardless of the characteristic of the
material that is stored in the tank (tanks
of this size are below the applicability
cut-offs for the SIP, subpart Kb, and the
HON). As a result, a new or existing
tank of this size has only a baseline
operating scenario, and no AOSs are
necessary. Similarly, no AOSs are
needed for tanks that are between 7.6
m3 and 38 m3 because only the SIP
requirements apply to these tanks
regardless of the liquid that is stored. A
tank that is between 38 m3 and 75 m3
needs a baseline operating scenario and
one AOS to enable switching between
storing a material that contains HAP and
one that does not. In both cases, the SIP
control requirements apply, but when
HAPs are stored the source must also
maintain the records required under the
HON. That is, when HAPs are stored, an
additional applicable requirement is
triggered for the tank.
Several operating scenarios are
needed for both new and existing tanks
between 75 m3 and 114 m3. The
possible scenarios for these tanks are
outlined in Table VI–2.
TABLE VI–2.—AUTHORIZED OPERATING SCENARIOS FOR NEW AND EXISTING STORAGE TANKS WITH CAPACITY BETWEEN
75 M3 AND 114 M3
1
2
3
4
5
6
7
.........................................
.........................................
.........................................
.........................................
.........................................
.........................................
.........................................
Are materials with HAPs
stored?
Tank size, V (m3)
Operating scenario No.
75
75
75
75
75
75
75
≤
≤
≤
≤
≤
≤
≤
V
V
V
V
V
V
V
≤
≤
≤
≤
≤
≤
≤
114
114
114
114
114
114
114
.....................
.....................
.....................
.....................
.....................
.....................
.....................
VP or VPH, as applicable
(kPa) a
No ......................................
No ......................................
No ......................................
No ......................................
Yes ....................................
Yes ....................................
Yes ....................................
VP < 15.0 ..........................
15.0 ≤ VP < 27.6 ..............
27.6 ≤ VP < 76.6 ..............
76.6 ≤ VP ..........................
VPH < 13.1 ........................
13.1 ≤ VPH < 76.6 ............
76.6 ≤ VPH ........................
Most stringent applicable
control requirements
SIP.
SIP.
NSPS.
NSPS.
SIP.
HON.
HON.
jlentini on PROD1PC65 with PROPOSALS2
a The following symbols are used in this column:
VP = stored liquid maximum true vapor pressure.
VPH = stored total HAP maximum true vapor pressure.
As seen in Table VI–2, seven
operating scenarios are approved for
new and existing storage tanks in this
size range. The source included this
table in its title V permit application,
along with the details about the
applicable requirements (including
control and MRRT requirements) for
each operating scenario. For each
41 The limit on tank size applies only to the
advance approved tanks. The source retains the
ability to construct tanks larger than 30,000 gallons,
but would have to go through the normal
preconstruction permitting to construct a larger
tank.
42 See section VI.A of this preamble and footnote
26 for more on the streamlining of applicable
requirements in a title V permit.
43 The HON applies to specified organic HAPs
that are a subset of the total HAP list. For this
example, we use ‘‘HAP’’ to refer to those HAPs
covered by the HON.
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jlentini on PROD1PC65 with PROPOSALS2
existing tank in this size range, the
source specified the baseline operating
scenario and designated the others as
AOSs. For any new tanks in this size
range, a baseline operating scenario
from the scenarios authorized in Table
VI–2 either was identified at the time of
minor NSR permitting (if known), or
will be identified at the time of
construction and operation. Table VI–2
is, therefore, a convenient means to
describe efficiently the individual
operating scenarios that are approved
with respect to the new and existing
tanks at the source.
The title V permit containing the
approved streamlined limits must also
identify the subsumed applicable
requirements. The permit also must
contain terms requiring the source to
keep an on-site log recording the use of
authorized AOSs. The log entries would
include, upon shifting to or from the
storage of HAP materials or materials of
different vapor pressure which
implicate different requirements, the
following: the size of the tank involved
(new or existing); the maximum true
vapor pressure of the stored material (if
no HAPs are stored) or the total HAP
maximum true vapor pressure (if the
stored material contains HAPs); the
control option employed; the applicable
requirements that apply (including
emissions limitations and MRRT
requirements); and the date that the
relevant storage commenced.
After an existing tank’s initial shift
from its baseline scenario, the on-site
log would identify at all times which
AOS was in effect for that tank. For a
new tank, the on-site log would be used
to record the initial baseline operating
scenario and any AOSs into which the
tank subsequently shifted. For example,
if the source switched from storing a
HAP-containing material to material
with no HAPs, the source would enter
that switch into the on-site log, giving
the date of the switch, identifying the
new AOS, and providing information
about which applicable requirements
(permit terms and conditions) were
implicated for that AOS.
E. What is the process for adding or
revising advance approvals, AOSs, and
ARMs in issued permits?
An advance approval, AOS, or ARM
may be added to a title V permit through
permit issuance or renewal or through
the permit modification process. When
an existing permit is to be modified, the
appropriate modification track
(significant or minor) depends on the
nature of the proposed advance
approval, AOS, or ARM or the proposed
revisions to them and whether it would
qualify as a minor permit modification.
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See 40 CFR 70.7(e)(2)(i). Note also that
the permit shield, where available, can
be extended to advance approvals,
AOSs, and ARMs added through a
significant permit modification, but not
to those added through minor permit
modification procedures (per existing 40
CFR 70.7(e)(2)(vi)). See section VI.C.3
above for more on AOSs and ARMs and
the permit shield.
F. How do the proposed AOS provisions
differ between parts 70 and 71?
Part 70 contains only the
requirements for State operating permit
programs and is not divided into
subparts. Part 71 contains two subparts.
Subpart A of part 71 contains the
general Federal operating permit
program, while subpart B contains
provisions for a limited, Federal title V
permit program to establish alternative
emissions limitations for early
reductions sources that have
demonstrated qualifying reductions of
HAP under section 112(i)(5) of the Act.
Thus, subpart A of part 71 is analogous
to the entire part 70.
A general difference between the part
71 and part 70 operating permit
programs is the identity of the
permitting authority. Under part 70,
non-Federal agencies are the permitting
authorities. A part 71 permit may be
issued by EPA, where there is not an
approved State program or where a State
has failed to revise a permit in response
to an objection from the Administrator,
or it may be issued by a permitting
authority that has been delegated
authority to issue part 71 permits on
behalf of EPA. Currently, part 71
permits are generally issued for sources
operating in Indian country.
For the most part, the proposed
revisions to the part 71 operating permit
program mirror exactly the proposed
revisions to part 70. That is, the
proposed language is identical, and the
sections of the rule that would be
revised differ only by being in part 71
instead of part 70. For example, we are
proposing the same language on AOS
permit content in 40 CFR 70.6(a)(9) and
71.6(a)(9). However, there is one place
where the structure of the part 71
operating permit program does not
parallel that of part 70, and therefore the
revisions proposed are different.
Specifically, 40 CFR 70.4(d)(3)(xi) is
one of the places in part 70 that we have
proposed to substitute the term ‘‘AOSs’’
for purposes of consistent terminology.
There is no analogous section in part 71,
so we are not proposing an analogous
revision.
We solicit comment on these topics
and all aspects of this proposal
regarding part 70. We also note that if
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52227
a commenter believes that additional or
different regulatory revisions are
needed, they should identify the
specific revisions and the basis for these
revisions.
VII. What changes are we proposing in
parts 51 and 52?
We propose to modify the major NSR
regulations in a limited way.
Specifically, we propose to allow a
number of emission activities to be
treated as a single emissions unit (i.e.,
a ‘‘Green Group’’). Emissions from each
of these activities would be routed to a
common emission control device
meeting BACT/LAER, and future
emissions and changes within the Green
Group would be approved over a 10year period in a major NSR permit. In
addition, we are proposing that Green
Groups not be subject to the provisions
of 40 CFR 52.21(j)(4) and 51.166(j)(4)
requiring reevaluation of BACT for
phased construction projects or of 40
CFR 52.21(r)(2) requiring continuous
construction to commence within 18
months. These provisions would remain
in effect for permits issued to emissions
units other than Green Groups. We are
proposing these changes because we
believe the anticipated benefits of
permitting Green Groups, similar to
those studied in pilot projects and
discussed in section IV.A, warrant
allowing the sources more time to
construct before the permit expires.
The approach we are proposing
represents an extension of our December
2002 NSR Improvement regulations and
reflects strategies that we believe ensure
environmental protection while
providing additional operational
flexibility to sources. In particular, we
intend Green Groups to complement the
use of plantwide emissions caps (e.g.,
PALs) by providing a flexible permitting
option for a section of a plant.44 Like
PALs, we propose that Green Groups
would be a mandatory minimum
element of a State NSR program under
which the permitting authorities retain
discretion as to when to approve
individual Green Groups requested by
44 The companies in two of our pilots conveyed
a clear desire to pursue an approach similar to the
Green Group options described in this proposal.
One of these facilities is a synthetic minor source
of VOC emissions for purposes of PSD applicability,
and is therefore not subject to major NSR. The
source did, however, agree to meet a best
technology requirement under the State’s minor
NSR program in order to authorize a range of
changes with VOC emissions conveyed to a highly
efficient carbon adsorption system. The second
facility went through major NSR to obtain
authorization for a wide spectrum of related
changes anticipated to occur in a complex of
buildings all ducted to a common state-of-the-art
control technology.
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sources.45 We also take comment on
whether instead the Green Groups
should be a voluntary rather than a
mandatory program element for States.
Sources that need to alter their
operations rapidly in response to market
pressures (including expanding
production) and that have controlled
portions of their plants to BACT/LAER
(either voluntarily or as part of their
efforts to meet applicable MACT or
other requirements) are good candidates
for the Green Group provisions. Such
well-controlled sources may have
limited growth potential under a PAL,
especially compared to sources with
less well-controlled baseline emissions.
Other candidates for Green Groups are
sources in which only a portion of the
facility accounts for all or nearly all
anticipated changes or large, complex
plants with many diverse operations
producing a variety of products. This
option for Green Groups would help
provide effective alternatives for the
diverse universe of sources potentially
subject to major NSR.
The Green Group provisions proposed
encourage a wide spectrum of sources to
construct specified types of changes for
a 10-year period with greater certainty
and flexibility in exchange for
implementing BACT/LAER, regardless
of whether or to what extent the source
may have been subject to the current
major NSR regulations. That is, the
Green Group provisions, if finalized,
would provide an alternative means to
comply with major NSR and not require
an evaluation of whether major NSR
would otherwise apply. For example, a
source might propose a Green Group
that would result in a net decrease in
actual emissions (i.e., application of
controls to meet BACT/LAER, as
applicable, reduces actual emissions by
an amount greater than the increased
emissions associated with the changes
authorized for the Green Group). Under
these circumstances, the source
voluntarily subjects to major NSR the
changes and existing operations
included within the Green Group,
presumably to obtain greater flexibility
and certainty in return for implementing
a BACT/LAER level of control.
jlentini on PROD1PC65 with PROPOSALS2
A. What are the benefits of Green
Groups?
For several reasons, we believe that
the environment and the public will
benefit from Green Groups. First, we
45 The major NSR rules refer to the ‘‘reviewing
authority,’’ while part 70 refers to the ‘‘permitting
authority.’’ For purposes of consistency with the
other sections of this preamble, we use the term
‘‘permitting authority’’ in this section. In these
discussions, this term is intended to have the same
meaning as ‘‘reviewing authority.’’
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believe that substantial environmental
benefits will occur, because a Green
Group requires all included emissions
activities to be controlled to the level of
BACT or LAER. The BACT or LAER
would apply to existing emissions
activities (which otherwise would
remain uncontrolled or be subject to less
stringent control requirements), as well
as to emissions activities that are
modified or added pursuant to the
Green Group authorization. In the
absence of a Green Group, existing
emissions activities would not be
subject to BACT or LAER controls until
such time as they were modified. Such
modifications might not ever occur, or
might occur far into the future. Even
where a modification did occur,
evaluated alone, many modifications
would likely not be subject to major
NSR. Some new emissions activities
might also not be subject to major NSR
because their emissions are below
applicability thresholds or because they
‘‘net out’’ of review. For example, a VOC
source might make one or more
unrelated modifications, each of which
are less than significant (i.e., would
result in increases in VOC emissions of
39 tpy or less). These modifications
would ordinarily not be covered by
NSR; however, when grouped together
as a Green Group, they would undergo
NSR and be subject to BACT/LAER.
Even when individual changes are
proved to be subject to major NSR, the
resulting BACT may in some cases be
less stringent than that required for a
Green Group. Considering the entire
Green Group, including all the
authorized future changes, in a single
major NSR action will drive a BACT
analysis toward the maximum level of
control due to the economies of scale
that occur in calculating the cost
effectiveness of controls. We believe
these environmental benefits will more
than offset the possibility that a future
BACT or LAER determination for new
approved expansion might be
marginally more stringent than the
BACT/LAER determination at the time
of the Green Group designation.
Moreover, we expect benefits to occur
from the better and more frequent type
and amount of monitoring that will be
required for Green Groups. Currently,
for a typical emissions unit subject to
major NSR, the permitting authorities
decide on a case-by-case basis the types
of MRRT appropriate for the permitted
emissions activities, consistent with the
underlying applicable NSR
requirements. We are proposing that a
Green Group be subject to MRRT
requirements that are patterned on the
existing requirements for PALs. In
addition, there are proposed safeguards
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to ensure that the air pollution control
device continues to function as
intended throughout the Green Group
designation period. These proposed
requirements will significantly improve
the monitoring data available to the
source, the permitting authority, and the
public, and thus, will better ensure
ongoing compliance.
Green Groups will also promote
greater administrative efficiency for
permitting authorities and sources,
because once a group of activities
qualifies, it will have increased
flexibility to make approved changes
rapidly in response to market demands
without needing to undergo additional
preconstruction permitting review. In
addition, permitting authorities benefit
from increased administrative
efficiency, because the Green Group
eliminates iterations of permitting
processes that produce little or no
environmental benefit.
B. What is a Green Group?
1. Defining the Scope of a Green Group
This notice proposes to define a Green
Group as one emissions unit that is
composed of designated emissions
activities ducted to one common air
pollution control device 46, 47, 48 that is
determined for this group to meet BACT
or LAER, as applicable. A Green Group
is a framework established under major
NSR for the advance approval of
anticipated changes within the group.
These changes can occur over a 10-year
phase, as described in the permit.
Separate Green Groups must be
established for emissions activities that
are ducted to separate air pollution
control devices.
46 The source may maintain a back-up control
device; however, all emissions from the Green
Group must be directed to a dedicated, common
pollution control device.
47 Emissions activities are the component
equipment that makes up the Green Group. For
example, a Green Group could include multiple
coating lines, and each individual coating line
could be considered an emissions activity within
the Green Group. Note that some or even several of
these might be individually regulated under one or
more other applicable requirements but are
combined into one emissions unit for purposes of
NSR.
48 In order to qualify for the Green Group
designation, all of the emissions activities that are
identified as part of the Green Group must be
conveyed to a common air pollution control device
to meet the BACT or LAER limit, as appropriate,
depending on whether the area is designated
attainment or non-attainment for the pollutant of
concern. Although this Green Group proposal
requires that the emissions from the Green Group
be ducted to a common air pollution control device,
consistent with existing EPA policy, the source can
use other control measures in addition to the
common control device to meet BACT or LAER.
Such additional measures can include P2, work
practices, or operational standards.
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In addition to current, designated
emissions activities, a Green Group may
include future changes (e.g.,
reconfiguration and/or expansion) to
these existing activities and/or the
addition of new emissions activities.
Either of these activities could result in
an increase in emissions, if the
permitting authority considers and
authorizes such future changes as part
of the NSR permitting process. We are
proposing that the NSR permit must
sufficiently describe the future new and
existing emissions activities that
comprise a Green Group and include
terms and conditions for them, such as
annual and short-term emissions limits.
These terms and conditions assure that
the Green Group activities will be
properly operated to protect air quality
as well as to meet BACT/LAER, as
applicable.
In its permit application, the source
must describe the new and existing
emissions activities to be included in a
Green Group in sufficient detail to allow
the permitting authority to determine
BACT or LAER (as applicable) for the
Green Group taken as a whole and to
conduct an ambient air impact analysis
to safeguard relevant ambient
increments and standards (including the
determination of any offsets necessary
in non-attainment areas) or any relevant
Class I areas. The application, therefore,
must provide information about the
current existing emissions activities and
the types of changes to be implemented,
including specifics on emissions
characteristics and the maximum total
amount of emissions that will be
generated by the Green Group’s
emissions activities after fully
implementing the changes. If the source
is unable to sufficiently describe the
new and existing emissions activities
that comprise the Green Group and the
associated emissions, the permitting
authority will not be able to issue a
major NSR permit with a Green Group
designation.
The information needed to describe
the type of changes authorized is
expected to vary on a case-specific basis
and will depend on the type of control
approach approved for BACT/LAER and
the emissions characteristics of the
included emissions activities and of the
changes which are permitted to occur to
them. That is, certain control devices
like carbon absorbers and scrubbers may
exhibit varying effectiveness in the
removal of different substances. As a
result, authorized changes subject to a
BACT/LAER determination requiring
such a control device would be
constrained to exclude emissions of
substances that cannot be controlled
sufficiently by the device. Moreover, the
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amount of detail needed to describe the
future changes may increase where
BACT is determined to be less than the
most stringent technology for the
proposed construction project(s).
Similarly, the scope of authorized
changes must be limited to ensure that
they are compatible with the relevant
monitoring, recordkeeping, and testing
provisions of the permit. In addition,
there may need to be restrictions on
how the changes occur to ensure the
effectiveness of the approved control
device. For example, in certain
situations, increased productive
capacity may need to be permitted to
occur in a manner which would not
overload the control device for the
Green Group.
The type of detail required in a permit
to describe the authorized changes in
the Green Group must also be sufficient
under the proposed approach to allow
the permitting authority to determine,
when a change subsequently is
implemented, whether the permitting
authority contemplated that change in
the scope of the advance approval
contained in the major NSR permit. As
a minimum, we expect that changes be
described relative to the existing
operations comprising the Green Group.
That is, the permit must contain a
detailed snapshot of the existing
emissions activities included in the
Green Group, and any approved changes
would then be described as categories of
changes to these baseline activities that
maintain their fundamental integrity.
Such changes might include: (1)
Changes in products; (2) changes in raw
materials; (3) reconstruction and/or
replacement of existing process
equipment; (4) increased capacity
(either as changes to existing equipment
or as new equipment); and (5) additions
of new production lines and/or new
support units.
When products or raw materials will
be changed, the description should
specify what the range of new products
or raw materials might be and their
compatibility to the existing emissions
controls. When equipment will be
added, reconstructed, or replaced, the
permit should specify whether capacity
might be changed and to what extent.
Depending on its potential relevance to
the BACT/LAER determination, the
description might specify the maximum
size and/or capacity of any changed or
new equipment. In some situations, it
might be necessary to describe the
different types of authorized changes
more specifically.
This proposed approach for
describing authorized future changes is
consistent with the approaches taken in
our evaluated flexible permit pilots and
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with our previously mentioned
recommendations for describing AOSs
in a title V permit.49 Provided that all
of the emissions activities identified as
part of the proposed Green Group are
vented through a common control
device and approved through the major
NSR permitting process, the source
would be authorized (for purpose of
major NSR) to implement over a 10-year
period the changes that are advance
approved in the permit without
triggering further NSR review. For
physical and operational changes a
source undertakes that are not included
in a Green Group, the applicability of
NSR to those changes would be
determined as these changes occur, in
accordance with existing major and
minor NSR procedures.
An emissions activity cannot be
included in a Green Group some of the
time and excluded at other times.
Stakeholders suggested allowing such
‘‘intermittently-included’’ activities
during pilot project discussions to
address emissions activities that are
subject to different applicable
requirements depending on their
operations. For example, a web-coating
operation might be subject to the
Pressure Sensitive Tape and Labels
NSPS (40 CFR part 60, subpart RR)
when manufacturing certain products,
and not subject to any applicable
requirement or emissions limitation
when manufacturing other products.
Some stakeholders suggested that such
a coating operation could be included in
the Green Group (and subject to the
Green Group control approach) when
subject to the NSPS, but excluded (and
not subject to control) when its
operations are not subject to the NSPS.
We rejected this approach because of
the increased complexity and the
significant additional recordkeeping
burden. Accordingly, after undergoing
major NSR as part of the Green Group,
the emissions activity remains subject to
the requirements of the major NSR
permit, including the BACT or LAER
emissions reduction requirements,
regardless of changes in the
applicability of any other requirement.
If a source removes a particular
emissions activity from an established
Green Group at any time during its 10year duration, the removed emissions
activity will be subject to major NSR.
For example, suppose that a Green
Group consists of four emissions
49 Note that additional detail to describe the new
and existing activities of a Green Group may be
necessary for title V purposes. For example, more
detail would be necessary to identify those
emissions activities included in the Green Group
that are also subject to other applicable
requirements (e.g., MACT or NSPS).
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activities and that the source proposes
to withdraw activity No. 4 from the
Green Group after its establishment. In
order to do so, the permitting authority
would subject activity No. 4 to major
NSR as if it were a new major
modification (i.e., contemporaneous
BACT/LAER, as applicable, and ambient
reviews). Simultaneously, the
permitting authority (in the same major
NSR action) would adjust downward
the emissions limit of the Green Group
(see discussion below) to account for the
amount of emissions previously
attributed to activity No. 4 (i.e., its
baseline actual emissions and any
emissions growth targeted to occur at
activity No. 4). In addition, the
permitting authority would verify that
the original BACT/LAER limit could be
met as it would now be applicable to the
remaining emissions activities.
2. Emissions Limits for Green Groups
In general, two types of emissions
limits must be set in the major NSR
permit for Green Groups: (1) An
emissions limit to constrain overall
emissions for the Green Group; and (2)
a limit to ensure that BACT/LAER
technology is being employed and is
effective (e.g., lbs/gal, percent
reduction). These two limits
complement each other and collectively
implement the core provisions of the
Green Group. The amount of any
emissions increase from authorized
changes would be limited by the annual
emissions cap and the BACT/LAER
emissions limitation, both of which
would be placed in the major NSR
permit.
An enforceable mass emissions limit
must be determined for the pollutant for
which the Green Group is established.
We propose that the total emissions
from the Green Group be limited by the
annual emissions limit (on a 12 month
total, rolled monthly basis) for the Green
Group pollutant. The annual emissions
limit would be set at the actual
emissions associated with all the
emissions activities included in the
Green Group and controlled to the
BACT/LAER level, as applicable. The
annual emissions limit would also
include any emissions increases that
result from changes to existing
emissions activities and/or changes to
add new emissions activities that are
authorized by the permit. The annual
limits and any necessary short-term
limits 50 for a Green Group must be set
50 The NAAQS and increments for some
pollutants are established over short-term periods
as well as annually. For example, annual, daily, and
3-hour NAAQS and increments are defined for
sulfur dioxide. Accordingly, some NSR permits
include emissions limits for these shorter periods.
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at a level demonstrated to safeguard
applicable ambient standards and
increments (i.e., NAAQS and PSD
increments).
We propose that the annual emissions
limit for a Green Group be developed in
two steps. The first step is to calculate
the group’s baseline for actual emissions
using the same methodology that is used
in setting a PAL under the existing
major NSR regulations. This baseline
would therefore equal the baseline
actual emissions (as defined in the
major NSR regulations) for all the
emissions activities in the group that
existed during a 24-month period
selected by the source within the 10
years preceding the Green Group permit
application, minus the emissions of any
of these existing activities that have
been shut down since the 24-month
period, plus the PTE of any emissions
activities added within the group since
the 24-month period. Baseline actual
emissions must be adjusted downward
for any non-compliant emissions during
the 24-month period and for any
emissions limitations that have become
applicable since the end of the 24month period. That is, a downward
adjustment is necessary if any legally
enforceable emissions limitation
restricts an emissions activity’s ability
to emit the Green Group pollutant or to
operate at levels that existed during the
selected 24-month period. See the
December 2002 preamble discussion of
baseline actual emissions at 67 FR
80195. (Note that the definition of
‘‘baseline actual emissions’’ differs
somewhat for electric utility steam
generating units (EUSGUs) and other
types of emissions activities. The
preceding discussion applies to nonEUSGUs.) In addition, these baseline
actual emissions must be adjusted
downward as necessary to reflect
application of the BACT/LAER to the
Green Group.
The second step in setting the annual
emissions limit for a Green Group is to
calculate the emissions increase from
any new emissions activities or planned
changes to existing activities that are
approved as part of the permit (i.e., an
emissions increase increment to address
the planned changes over a 10-year
period.) This would be added to the
baseline actual emissions level
determined in the first step. Thus, the
total Green Group annual emissions
limit should reflect the actual emissions
associated with all new and existing
emissions activities included in the
Green Group, all of which are controlled
to the BACT/LAER level, as applicable.
In an attainment area, in reviewing
the application, the permitting authority
should weigh such factors as the
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available PSD increment(s) in the area
in determining whether to approve the
annual limit proposed by the source for
the Green Group. In a nonattainment
area, the authorized emissions increase
must be offset at the ratio prescribed by
the Act or the applicable State, Tribal,
or Federal implementation plan.
To the extent that they can be
quantified, fugitive emissions also must
be addressed for Green Groups as
required under the Act and by EPA
according to applicable major NSR
regulations and requirements and
guidance. This includes determining
fugitive emissions from all existing
emissions activities in the Green Group,
as well as all increases in fugitives and
maximum total fugitive emissions that
will be generated in the future by the
emissions activities in the Green Group.
Such treatment of fugitive emissions is
intended to be the same approach as
that currently required for PALs.
An emissions limit or performance
specification separate from the Green
Group emissions limit determined
above also must be set to reflect the
application of BACT or LAER, as
applicable. The format for these limits
can vary (e.g., pounds of emissions per
material input or per product output; or
a percent removal efficiency) but are
typically different from the tpy format of
the limit applying to total annual
emissions. In some cases, separate,
additional BACT/LAER limits may be
necessary to govern low concentration
situations (e.g., the source would be
required to meet either 98 percent
removal efficiency or a 20 parts per
million (ppm) outlet concentration) and
to address startup, shutdown, and
malfunction situations.
We also propose that a Green Group
may meet the applicable BACT or LAER
level of control through use of P2
alternatives for component emissions
activities during some periods of
operation instead of always sending all
emissions to the common air pollution
control device. Each of the P2
alternatives must independently qualify
as achieving a BACT or LAER level of
control in the major NSR permitting
process. For example, an emissions
activity such as a paint spray booth
operation would be ducted to a common
air pollution control device such as a
thermal oxidizer to control VOCs from
multiple emissions activities in a Green
Group. As a P2 alternative, BACT or
LAER might be established based on the
use of compliant materials 51 in the
51 For surface coating operations, ‘‘compliant
materials’’ means coatings and solvents that are
formulated to meet emissions limits without need
of add-on controls. For example, coatings may be
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spray booth operation. In this case, we
propose that each of the included
emissions activities must have ductwork
extending to the common air pollution
control device, but the source would be
allowed to bypass the control device
during periods when the source elects to
use P2 consistent with the BACT or
LAER determination on compliant
materials. Notwithstanding, at all times,
all activities included in the Green
Group would be meeting a BACT (or
LAER as applicable) level of control.
We believe that providing for a P2
alternative will encourage P2 at sources
that wish to obtain a Green Group
designation and provide an opportunity
for sources that are pursuing P2 to adopt
a Green Group. Accordingly, we are
soliciting comment on whether such an
option is appropriate and should be
included in the Green Group program.
We further request comment on whether
this proposal goes far enough in
encouraging P2. In particular, we take
comment on whether we should allow
a Green Group to be based on use of a
P2 approach, rather than a common air
pollution control device.
For the emissions activities that
comprise the Green Group, we are not
proposing to require that each emissions
activity that is part of the Green Group
designation be limited to a specific tonsper-year allocation. Instead, we propose
that the annual aggregate limit is
acceptable for the emissions activities
that comprise the Green Group. For
example, if each of the five emissions
activities that are part of a Green Group
contributes 50 tpy to the total annual
aggregate limit of 250 tpy, we are
proposing that the Green Group be
subject only to a limit of 250 tpy for
these emissions activities. A permitting
authority, therefore, should not require
a 50 tpy limit on each of the five
emissions activities.52 This is because
for PSD purposes, the source must
determine BACT based upon the total
amount of annual emissions, and the air
quality impacts associated with such
emissions (which all are emitted from
the stack of the common air pollution
control device) are accounted for in the
NSR permitting process. Comparable
reasoning applies for nonattainment
major NSR purposes. We solicit
comment on whether this approach is
appropriate or whether there are other
formulated with high solids content and low VOC
content.
52 In some cases, a source may have previously
taken an emissions limit on a new or modified
emissions unit to remain below major NSR
applicability thresholds (often referred to as an
‘‘(r)(4) limit’’ based on § 52.21(r)(4)). Once the unit
is included with a Green Group, it has gone through
major NSR, and the (r)(4) limit will no longer apply.
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considerations we should take into
account.
Changes in emissions at ancillary
units not included in the Green Group
but serving it (such as storage tanks or
utilities) must be accounted for in the
air quality analysis conducted to
evaluate ambient air quality and
increment protection to the extent such
emissions changes are required to be
considered under the existing NSR
regulations.53 Ultimately, the permitting
authority must determine the extent to
which the requested expansion will be
allowed under major NSR, taking into
account the demonstrated need of the
source, public comments received, and
the air quality status of the affected area.
In some cases, a source may have
previously taken an emissions limit on
a new or modified emissions unit to
remain below major NSR applicability
thresholds (often referred to as an ‘‘(r)(4)
limit’’ based on 40 CFR 52.21(r)(4)).54
The major NSR rules provide that if
(r)(4) limits are relaxed, the associated
emissions unit must undergo major NSR
review ‘‘as though construction had not
yet commenced on the source or
modification.’’ We propose to clarify,
without rule revision, the interface
between (r)(4) limits and Green Groups
as follows: When a unit with an (r)(4)
limit is included as one of the emissions
activities in an application for a Green
Group, the (r)(4) limit no longer applies,
provided that the NSR review process
considers the unit as if construction had
not yet commenced on it.55 Moreover,
any (r)(4) limit would no longer apply
even after the expiration of any Green
Group.
Under the current NSR regulations, an
emissions change is only creditable to
the extent the Administrator has not
previously relied on it in issuing a major
NSR permit. See 40 CFR 52.21(b)(3)(i).
Accordingly, emissions increases and
decreases that occur at the emissions
53 The EPA has issued a Notice of Proposed
Rulemaking that addresses, in part, the issues of
‘‘debottlenecking’’ and ‘‘increased utilization.’’ See
71 FR 54235, September 14, 2006. In this
rulemaking on flexible air permits, we do not
intend to change current requirements related to
‘‘debottlenecking’’ or ‘‘increased utilization,’’ but
we will follow, as applicable, any final rule changes
occurring as a result of the September 2006
proposal.
54 Parallel requirements are found at 40 CFR
51.165(a)(5)(ii) and 51.166(r)(2).
55 The baseline actual emissions for a unit with
an (r)(4) limit are calculated just as for any other
emissions activity included in a Green Group,
complete with the reduction for the effect of the
required BACT/LAER control. However, such units
may be among the emissions activities with
authorized future physical or operational changes,
and emissions from such units could subsequently
increase (as part of the authorized emissions
increase increment), but under BACT/LAER
controls.
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52231
activities in a Green Group during the
effective period of the Green Group
designation are not included in netting
calculations to determine whether
changes that occur at the emissions
units outside the Green Group result in
a major modification. However, if the
source reduces actual emissions from
the Green Group below the emissions
limit established for the Green Group in
its NSR permit, the source may generate
a credit for the difference between the
permitted limit that qualified the unit as
a Green Group and any new, lower
emissions limitation established, if such
reductions are surplus, quantifiable,
permanent, and enforceable from a
practical standpoint.56 If however, an
established Green Group wishes to
increase its emissions beyond its
permitted tpy limit, reductions achieved
by units outside the Green Group cannot
be used to generate emissions
reductions to net the Green Group out
of NSR. If an established Green Group
wishes to increase its emissions, it must
go through NSR again to establish a new
limit, which would be effective for a
new 10-year timeframe. In addition, we
also propose to add a restriction that no
credit can be generated from eliminating
emissions increases that were
authorized under the Green Group
permit but never realized. Without this
restriction, sources would be allowed to
generate credits for authorized
expansion that never occurred.
In nonattainment areas, sources are
required to obtain offsetting emissions
reductions for the significant emissions
increases that are authorized under a
major NSR permit. Depending on the
nonattainment pollutant and
classification of the nonattainment area,
the source may be required to obtain
offsets in excess of the emissions
increase at a specified ratio. For
example, in accordance with the
existing NSR requirements, in a serious
ozone nonattainment area, a source
must obtain VOC offsets in an amount
1.2 times the significant VOC emissions
increase. A source that applies for a
Green Group designation in a
nonattainment area must obtain offsets
for the approved increase in emissions
of the Green Group pollutant (i.e., the
difference between the level approved
in the Green Group permit and the
baseline actual emissions of the group).
Under existing NSR requirements,
offsets must be federally enforceable at
the time the major NSR permit
designating the Green Group is issued,
in accordance with section 173(a) of the
CAA, but need not be achieved until the
56 Such credits in order to be used as an
emissions offset must also be federally enforceable.
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new or modified source commences
operation, consistent with section 173(c)
of the CAA. We propose that for Green
Groups, the offsets must be in effect by
the time the first authorized change
among the activities in the Green Group
(e.g., equipment modification or
addition) commences operation. To
simplify the process and recordkeeping,
and to assure that offsets are in place as
required, we propose that the entire
amount of offsets required by the permit
must be in effect at the time that the first
authorized change (e.g., modified or
added emissions activity) begins
operation. Alternatively, we seek
comment on whether it is only
necessary to require the source to obtain
offsetting emissions reductions in
sufficient quantity to offset: (1) The
actual changes within the Green Group
as they occur; or (2) each phase of
construction before its operation.
In some cases, a source with an
established Green Group may
subsequently request the permitting
authority to allow the addition of greater
emissions than are permitted by the
existing annual emissions limit. Here,
we propose that the permitting authority
be able to either: (1) Establish a higher
annual emissions limit to accommodate
the desired new emissions increase as
part of a comprehensive major NSR
process (this process would reestablish
the Green Group, including a
reevaluation of the prior BACT/LAER
determination); or (2) terminate the
Green Group while retaining its
emissions limits and other requirements
and then subject the emissions of new
project(s) to the applicable NSR process.
Similarly, if a source with a Green
Group exceeds its Green Group
emissions limit, then the source will be
subject to appropriate enforcement
action. In addition, the source would be
subject to enforcement action for any
violations of other applicable
requirements (e.g., MACT, NSPS) that
would also apply to emissions activities
included in the Green Group.
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3. Monitoring, Recordkeeping,
Reporting, and Testing (MRRT)
Requirements for Green Groups
As mentioned, the major NSR review
process must also determine the level of
MRRT to assure compliance with both
the control technology requirement and
the emissions limit(s). A source must
monitor all emissions activities that
comprise the Green Group to ensure
compliance with the Green Group limit.
These monitoring, recordkeeping, and
reporting requirements are incorporated
into the NSR permit that establishes the
Green Group.
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As explained above, in December
2002, we promulgated revisions to the
major NSR program, which included,
among other things, MRRT requirements
for tracking emissions associated with a
PAL.57 In these proposed regulations,
the same MRRT we promulgated in
December 2002 for PALs would also be
required to track a source’s compliance
with the Green Group emissions limit
set forth in the major NSR permit.
Further, we are proposing additional
MRRT provisions to assure that the
common air pollution control device
achieves BACT or LAER. More
specifically, the permit must require the
owner or operator to monitor and record
data sufficient to ensure that the
common control device for the Green
Group accommodates emissions
resulting from the emissions activities
that comprise the Green Group and that
it achieves the level of emissions
reduction required under the applicable
BACT or LAER requirement.58
We are not proposing to require a
source to notice individual changes at
Green Groups. However, changes which
are also subject to a MACT standard or
NSPS may well be required to file a
notice under the General Provisions
requirements of those programs. State
permitting authorities may under other
regulatory authorities require additional
records and notices for certain changes
(e.g., notices for new units under State
air toxics program, or a notice for a new
emissions unit added to the site of a
source with a title V permit under an
approved off permit procedure) to
assure compliance under these other
authorities. In addition, we propose that
the source submit a semi-annual report
that, in part, contains a list of any
emissions activities included in the
Green Group that were added during the
preceding 6-month period. We
encourage permitting authorities to
combine this report with the 6-month
monitoring report otherwise required
under part 70 (see 40 CFR
70.6(a)(3)(iii)(A)). We request comment
on this approach to recordkeeping,
reporting, and notification
requirements. In particular, we solicit
comment on the appropriateness of
applying the mentioned 2002 PAL
57 See 67 FR 80221 for a discussion of the MRRT
requirements promulgated for PALs by the Agency
in December of 2002.
58 Note that BACT/LAER requirements in terms of
percent reduction can be difficult or impossible to
achieve during periods of low or dilute flow. Where
a percent reduction requirement is imposed, we
recommend that the BACT/LAER determination
include an alternative concentration standard for
such periods. For example, BACT/LAER for VOC
control might be 98 percent reduction or an outlet
concentration of 20 ppm by volume on a dry basis.
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monitoring requirements to Green
Group emissions limits.
4. Public Participation for Green Group
Designations
Because Green Groups must be
established in a major NSR permitting
action, the public is assured of an
opportunity to participate in the
process. Major NSR regulations require
the permitting authority to notify the
public when it makes a preliminary
determination regarding a permit
application, to make the application and
associated materials available for public
inspection, and to provide an
opportunity for a public hearing and for
a written comment period of not less
than 30 days.59 In the case of a proposed
Green Group permit, the annual
emissions limit that would be
established for the Green Group
highlights the maximum possible
annual emissions increase for public
review. The other aspects of the
proposed Green Group also would be
highlighted for comment, including the
preliminary BACT/LAER determination,
description of anticipated expansion,
and the proposed requirements for
monitoring, recordkeeping, and
reporting.
In addition to the opportunity for
public participation typically provided
consistent with our major NSR
regulations, we recommend that the
permitting authority consider using its
discretion to enhance the public
participation process as necessary to
provide adequate review opportunity for
individual Green Group permits. We
expect that this may be advisable when
the first Green Groups in an area are
being established or when unique and/
or complex issues arise in a particular
case. See section IV.C above for
additional discussion on the types of
enhanced public participation and
when it might be appropriate.
5. Duration and Renewal of the Green
Group Designations
We propose that the Green Group
designation last for a single 10-year
period. Any emissions activities that are
advance approved and constructed
during the effective period of the Green
Group designation benefit from Green
Group flexibility. At the end of the 10year period, the original Green Group
designation ends.
After 10 years, the source may apply
for a new Green Group designation by
going through the same procedures as
for the initial Green Group designation,
59 See 40 CFR part 124 for permits issued under
§ 52.21. See § 51.161 for permits issued under State
programs approved pursuant to §§ 51.165 and
51.166.
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including going through a new major
NSR permitting exercise and a new
BACT/LAER determination. To avoid a
gap between the expiration of the initial
Green Group designation and the
effective date of a new designation, we
propose a renewal process similar to the
process for PALs. Specifically, a source
that wishes to reestablish its Green
Group must submit a major NSR
application to the permitting authority
at least 6 months prior to, but not earlier
than 18 months from, the expiration
date of the Green Group. If the source
submits a complete application within
this period, the existing Green Group
requirements would continue to be
effective until the new major NSR
permit reestablishing the Green Group is
issued.60 We take comment on the need
to require an earlier submittal time (i.e.,
earlier than 6 months prior to
expiration) given that a BACT/LAER
reevaluation is involved.
If the applicant does not wish to
reestablish the Green Group
designation, the source would simply
allow the designation to expire and then
become subject to the major NSR
applicability test for future changes.61
However, the major NSR permit does
not expire, and the emissions unit
defined by the Green Group would
remain permanently an emissions unit
for purposes of major NSR, subject to
the BACT or LAER control requirement,
annual emissions limit (and any shorterterm limits), and MRRT requirements
imposed by the Green Group permit. We
take comment whether to allow the
source to divide up the Green Group
into smaller emissions units and to
allocate the emissions limit
correspondingly.
We are proposing the 10-year duration
of a Green Group designation for two
reasons. First, we believe that this time
60 In order to streamline the process to update as
necessary the corresponding title V permit, the
permitting authority might: (1) Structure the permit
to retain the initial BACT limit and support
conditions unless affirmatively revised; and (2)
revise the title V permit in parallel to revising the
NSR permit or use an ‘‘enhanced NSR’’ process to
do so in order to optimize use of comment periods
and opportunities for public hearings.
61 We expect that in most cases this will be the
actual-to-projected-actual applicability test adopted
in the December 2002 NSR Improvement
rulemaking. The actual-to-projected-actual test is
currently in effect in all jurisdictions where § 52.21
applies, including in States and Indian country. For
nonattainment major NSR and SIP-approved PSD
programs, States are currently in the process of
revising their SIPs to incorporate the actual-toprojected-actual test (or some other preferred
approach if they can demonstrate that it is at least
as stringent as the actual-to-projected-actual test).
Thus, the actual-to-projected-actual test (or an
approved alternative approach) should be in effect
in all jurisdictions by the time that Green Groups
begin to expire.
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frame represents a balance between the
useful life of the emissions control
system and the time frame in which
additional major NSR review is likely to
result in little, if any, added
environmental benefit.
Prior to the December 2002 NSR
Improvement rulemaking, we examined
the useful life of air pollution control
devices. Based on the guidelines for
equipment life for nine commonly used
emissions control technologies,62 we
determined that a reasonable average
equipment life is 15 years. See 87 FR
80229. We also looked at the
incremental improvement in control
technology over time. Over the 15-year
period that we studied (1988–2002), we
did not find any data to suggest that
improvements in control technology are
occurring that are of sufficient
magnitude to lead to BACT
determinations requiring replacement of
control systems on existing units that
are equipped with BACT.63 Thus, we
believe that 15 years likely represents a
reasonable balance between the useful
life of air pollution control devices and
the time frame in which a new BACT
determination would require additional
emissions control. Ten years represents
a more environmentally cautious
approach to balancing these factors.
Second, a 10-year duration for a Green
Group is supported by the rationale we
used in choosing a 10-year period for
the duration of PALs. For PALs we
concluded that a 10-year period was
necessary to ensure that the normal
business cycle would be captured
generally for any industry. See 67 FR
80216. The PAL’s 10-year period also
was intended to balance the need for
regulatory certainty, the administrative
burden, and a desire to align the PAL
renewal with the title V permit renewal.
See 67 FR 80219. These reasons also
apply with equal force in guiding the
selection of a similar 10-year period for
Green Groups.
As a practical matter, we realize that
the ‘‘ideal’’ duration for a Green Group
will vary somewhat by emissions
control technology and by pollutant;
however, we believe using a single time
frame will provide simplicity in the
rules. We have chosen to propose a 10year duration for Green Groups to
maintain consistency with PALs and to
62 Vatavuk, William, ‘‘Part II, Factors for
Estimating Capital and Operating Costs,’’ Chemical
Engineering, Nov. 3, 1980.
63 See ‘‘Supplemental Analysis of the
Environmental Impact of the 2002 Final NSR
Improvement Rules,’’ EPA, November 21, 2002, pp.
10–11 and Appendices C and D. Available at
https://www.epa.gov/NSR/documents/nsranalysis.pdf.
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52233
maximize the environmental benefits of
Green Groups.
We are also taking comment on a 15year duration for a Green Group
designation. As discussed above, we
believe that air pollution control
technology typically is quite stable
during this period. In addition, the fact
that BACT/LAER is determined for the
entire Green Group taken as a whole
(including authorized expansions),
rather than for individual changes
piecemeal, is likely to result in more
effective and more costly controls than
would be applied under mainstream
major NSR permitting. As a result, it is
even less likely that a subsequent
BACT/LAER determination at a Green
Group would require a new control
device within a 15-year period. Thus,
we believe that a 15-year period could
also represent a reasonable and
appropriate duration for Green Groups.
We propose that the effective date of
a Green Group designation would be the
effective date of the major NSR permit
that designates the Green Group. We
propose that the Green Group
designation lasts for a period of 10 years
from the effective date.
If construction or modification of a
control device is required by the BACT/
LAER determination in the Green Group
permit, no advance approved changes in
the permit are allowed to occur before
that construction or modification is
completed. That is, new and modified
emissions activities within the Green
Group may not be operated until the
new or modified control device is in
operation. This will result, in effect, in
a reduction of the 10-year duration for
the Green Group by the length of time
between the effective date of the permit
and the beginning of operation of this
control device in order to comply with
BACT/LAER.
We do not believe, however, that the
unchanged, existing emissions activities
in the Green Group should be required
to cease operation while the control
device is constructed or modified. This
would be the outcome if these emissions
activities were required to meet the
BACT/LAER emissions limitation(s) on
the effective date of the Green Group
permit. Accordingly, we are proposing
that, where the BACT/LAER
determination requires a new or
modified control device, the Green
Group permit may provide that the
existing emissions activities within the
Green Group are not required to meet
the BACT/LAER emissions limitation(s)
or the annual emissions cap for the
Green Group until the new or modified
air pollution control device is in
operation. In the interim, such
emissions activities may continue to
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jlentini on PROD1PC65 with PROPOSALS2
meet pre-existing emissions limitations.
In contrast, where the existing control
device has been determined to represent
BACT/LAER without modification, all
existing emissions activities must meet
BACT/LAER upon the effective date of
the Green Group permit.
A situation that can result in
termination of a major NSR permit
under the existing NSR rules is related
to the timely commencement of the
program of construction authorized by
the permit. Section 52.21(r)(2) of the
existing federal PSD rules provides that
approval to construct shall become
invalid if construction is not
commenced within 18 months after
receipt of such approval, if construction
is discontinued for a period of 18
months or more, or if construction is not
completed within a reasonable time.
The Administrator may extend the 18month period upon a satisfactory
showing that an extension is justified.64
We are proposing to exclude Green
Groups from the section 52.21 (r)(2)
provisions. However, we are also
proposing a new safeguard for those
Green Groups that rely on a new or
upgraded BACT/LAER air pollution
control device. Although the Green
Group designation becomes effective on
the effective date of the permit, the
source must complete construction on
the new air pollution control device
before any changes advance approved in
the permit can be operated. See section
VII.D for more discussion of the
rationale for this proposal.
We believe that Green Group
activities also should be exempted from
the paragraph (j)(4) provisions of both
40 CFR 52.21 and 51.166. Currently, the
(j)(4) provisions require for phased
construction projects that the BACT
determination be reviewed and
modified as appropriate at the latest
reasonable time which occurs no later
than 18 months prior to commencement
of construction of each independent
phase of the project. There is no need
to evaluate the interdependence of
changes since, under the proposed
Green Group approach, the Green Group
is considered one ongoing program of
change over a 10-year period.
Accordingly, we propose to remove the
applicability of 40 CFR 52.21(j)(4) and
51.166(j)(4) from Green Groups. See
section VII.D for our rationale
concerning this proposal.
64 The Federal PSD rules apply in jurisdictions
that do not have their own approved PSD programs,
including a number of States (to which we have
delegated implementation or in which EPA directly
administers the program) and in Indian country.
Many State and local major NSR programs include
similar provisions.
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6. How are Green Groups similar to
PALs?
We also take comment on whether a
Green Group is a form of PAL. As noted
previously, the Green Group establishes
an actual emissions-based limitation for
a logical collection of emissions
activities (i.e., all those ducted to a
common control device). The Green
Group approach relies upon several of
the same principles and techniques
used in establishing and managing
growth for sources with PALs and other
types of emissions caps. We
experimented with PALs and emission
caps as part of the pilot program and
have, as a result, a significant amount of
development, implementation, and
emissions tracking experience using
these approaches. Specifically, a Green
Group is established based on the actual
emissions, plus authorized emission
increases associated with the addition
or modification of emissions activities.
The authorization of additional capacity
for new or modified emissions activities
provides sources with the ability to
respond to market changes and
eliminates administrative burden
associated with multiple permit actions.
In exchange, the emissions associated
with a Green Group are constrained by
an emissions cap for an established
period of time. It offers substantial
environmental benefits by assuring that
all emissions activities within the group
are well-controlled and eliminates the
ability of the Green Group to undertake
insignificant emissions increases that
could go unreviewed as separate,
independent projects.
Although the Green Group builds an
emissions increase into the initial cap,
it does so in a way which complies with
all the requirements that we established
for increasing a PAL. Moreover, the
approved increase in actual emissions is
allowed only if it is due to the
expansion authorized to occur within
the Green Group, since the BACT/LAER
requirement prevents any backsliding in
the control of existing emissions
activities in the Green Group. Thus,
subsequent changes in the Green Group
whose actual emissions (in combination
with those of existing activities
included in the Green Group) do not
exceed the Green Group emissions limit
and will be ducted to a control device
determined to meet BACT/LAER, as
applicable, have already been regulated
under major NSR in anticipation of the
changes being made. We solicit
comment as to whether the Green Group
is a permissible application of the PAL
principles as applied to a logical
collection of emissions activities that
are ducted to a common control device
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and, if so, what increase in emissions
for existing emissions activities and/or
increases for new emissions activities
can be authorized to occur under a
major NSR permit. We also seek
comment on the potential applicability
of these same PAL principles to a
proposed Green Group that involves
only new emission activities ducted to
a common pollution control device
authorized under major NSR.
C. How is a Green Group designation
incorporated into a title V permit?
Major and minor NSR permit terms
and conditions are applicable
requirements for purposes of title V. As
such, they must be incorporated into the
source’s title V permit. These proposed
major NSR rules list the required
content for a NSR permit that designates
a Green Group. Part 70 requires that
these permit terms and conditions be
incorporated into the source’s title V
permit according to the provisions of
the applicable title V permit program
(but no later than when the title V
permit is renewed). One potential route
for incorporating these terms and
conditions into the title V permit is
through an administrative amendment,
if an ‘‘enhanced’’ NSR process is used
to designate the Green Group. See 40
CFR 70.7(d)(v). This mechanism is
available if the EPA-approved NSR
program includes both procedural
requirements substantially equivalent to
the requirements of 40 CFR 70.7 and
70.8 and substantive requirements
substantially equivalent to those
contained in 40 CFR 70.6.65
We expect that in many cases, the
emissions activities included in the
Green Group will be subject to other
applicable requirements, such as SIP
requirements, NSPS, and/or MACT
standards. In such cases, concurrently
with the major or minor NSR process, as
applicable, the source can seek to
modify its title V permit to include
baseline operating terms and conditions
and/or AOSs (as necessary) to address
and assure compliance with all
applicable requirements that apply to
the authorized emissions activities
comprising the Green Group, including
any advance approvals. Because the
BACT or LAER requirement that applies
to the Green Group typically is the most
65 Section 70.6 describes the required elements of
permits issued under part 70 such as emissions
limits, applicable requirements, permit duration,
and MRRT. Section 70.7 describes the process for
issuing, renewing, reopening, and revising permits.
Section 70.8 describes the process by which EPA
will review permits and State programs, object to
permits, and act on public petitions. It also requires
the permitting authority to give notice of each draft
permit to any affected State and to consider its
comments.
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stringent of the applicable requirements,
Green Groups are often good candidates
for streamlining as mentioned in section
VI.A, footnote 26, and section VII.F of
this preamble.
This proposal provides permit
flexibility in that a source can obtain a
Green Group through the major NSR
permit process (which constitutes the
required NSR authorization for future
changes in the group) and, at the same
time, modify its title V permit to include
the Green Group and AOSs, as
necessary, to address the other
applicable requirements that apply to
the emissions activities in the Green
Group. The approval of the Green Group
changes with regard to all relevant
permitting requirements means that the
source can implement these changes
authorized under protection of the
permit shield without seeking any
further title V approvals.
D. What is the legal rationale for Green
Groups?
The basic CAA provisions
establishing permitting requirements for
attainment/unclassifiable areas (the PSD
requirements) under part C of title I, and
for nonattainment areas under part D of
title I, are the basis for this action. With
respect to the PSD requirements, CAA
section 165(a) provides, in relevant
part—
jlentini on PROD1PC65 with PROPOSALS2
No major emitting facility on which
construction is commenced after the date of
the enactment of [the 1977 CAA
Amendments], may be constructed in any
area to which this part applies unless—
(1) a permit has been issued for such
proposed facility in accordance with this part
setting forth emission limitations for such
facility which conform to the requirements of
this part * * *
The term ‘‘construction’’ is defined to
refer to both construction of a new
source and ‘‘modification’’ of an
existing source. See CAA section
169(2)(C).
With respect to the nonattainment
major NSR requirements, section
172(c)(5) of the Act provides that
nonattainment SIP provisions ‘‘shall
require permits for the construction and
operation of new or modified major
stationary sources anywhere in the
nonattainment area, in accordance with
section 173.’’ Section 173(a), in turn,
provides that ‘‘permits to construct and
operate may be issued if [certain
requirements are met].’’
These PSD and nonattainment major
NSR provisions contain no specific
requirements concerning the maximum
length of time that may elapse between
the issuance of the permit and the
beginning of construction, the
maximum length of time that the
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construction may take, whether the
construction may occur in phases, or the
maximum period of time that may
elapse between any construction phases.
By comparison, other, related major
NSR provisions of the Act do contain
timing requirements. For example, for
PSD purposes, section 165(c) directs the
permitting authority to grant or deny the
permit within one year after the date of
filing of the completed permit
application. As a second example, for
nonattainment major NSR purposes,
section 173(a)(1)(A) directs that
emission offsets must be obtained ‘‘by
the time the source is to commence
operation.’’ The lack of specific timing
requirements concerning construction
in the relevant provisions of sections
165(a), 169(2)(C), 172(c)(5), and 173(a)
means that EPA has flexibility in
determining the circumstances under
which construction timing requirements
are necessary, and in promulgating
regulations to that effect.66
By notice dated June 19, 1978, we
promulgated certain requirements
concerning phased construction. See 43
FR 26380. Under those requirements:
Approval to construct shall become invalid
if construction is not commenced within 18
months after receipt of such approval, if
construction is discontinued for a period of
18 months or more, or if construction is not
completed within a reasonable time. The
Administrator may extend the 18-month
period upon a satisfactory showing that an
extension is justified. This provision does not
apply to the time period between
construction of the approved phases of a
phased construction project; each phase must
commence construction within 18 months of
the projected and approved commencement
date.
66 It should be noted that for purposes of section
165(a), as quoted above, the term ‘‘commenced’’ is
defined, under section 169(2)(A), as follows: ‘‘The
term ‘commenced’ as applied to construction of a
major emitting facility means that the owner or
operator has obtained all necessary preconstruction
approvals or permits required by Federal, State, or
local air pollution emissions and air quality laws or
regulations and either has (i) Begun, or caused to
begin, a continuous program of physical on-site
construction of the facility or (ii) entered into
binding agreements or contractual obligations,
which cannot be canceled or modified without
substantial loss to the owner or operator, to
undertake a program of construction of the facility
to be completed within a reasonable time.’’ This
definition of ‘‘commenced,’’ in context, served the
purpose of subjecting a source to the PSD
requirements when the source undertook the
actions included in the definition, and thereby
‘‘commenced’’ construction, even if EPA had, by
regulations promulgated prior to enactment of the
PSD provisions in the 1977 Clean Air Act
Amendments, attempted to exempt the source from
regulatory PSD review. For present purposes, the
fact that Congress defined ‘‘commenced’’ to include
construction timing requirements for the narrow
purpose described above, but did not apply such
requirements to construction more broadly, further
supports our view that we have discretion in
applying construction timing requirements.
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52235
See 40 CFR 52.21(r)(2).
For phased construction projects, the
determination of best available control
technology shall be reviewed and modified
as appropriate at the latest reasonable time
which occurs no later than 18 months prior
to commencement of construction of each
independent phase of the project. At such
time, the owner or operator of the applicable
stationary source may be required to
demonstrate the adequacy of any previous
determination of best available control
technology for the source.
See 40 CFR 52.21(j)(4) and
51.166(j)(4).
We stated as the reason for these
requirements:
The Administrator is concerned about the
issuance of permits for phased construction
projects that would have the effect of
‘‘reserving’’ the increment for a single source,
thereby limiting growth options in the area.
The options are to not issue phased
construction permits at all or to limit the
conditions under which a phased
construction may reserve an increment well
into the future. The Administrator intends to
implement the latter option when plans for
a phased project are certain and well-defined.
One mechanism to be used is to reassess the
BACT determination for the later phases of
the project prior to construction to ensure
that the most up-to-date control technology
will be used. The Administrator will specify
at the time that the original permit is issued
which BACT determinations will be
reassessed. The Administrator may also
adopt regulations in the future to deal with
this issue more comprehensively.
See 43 FR 26396.
The EPA proposes to exclude Green
Groups from the requirements of 40 CFR
52.21(r)(2), 52.21(j)(4), and 51.166(j)(4)
on policy grounds. The Green Group
designation provides a vehicle for a
source willing to describe its
construction plans in its permit, as well
as employ BACT/LAER emission
controls and comply with other major
NSR requirements, in return for the
ability to make a variety of changes
without the burdensome process of
iterative permitting actions. We believe
that making such changes (as authorized
within Green Groups) can be fairly
described as merely implementing the
major NSR permits as approved. That is,
no authorized changes over the 10-year
period need to be reevaluated as a
possible new modification since those
changes have already been subjected to
major NSR, including a determination of
BACT/LAER requirements and the
approval of ambient air quality impacts
or the acquisition of offsets. We believe
that the exclusion of Green Groups from
these provisions is needed to provide an
adequate level of certainty and
flexibility to participating sources (i.e.,
the certainty that a BACT/LAER
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determination will last a reasonable
duration). This proposal would ensure
the basic premise of the Green Group
approach (i.e., sources are just making
those changes contemplated and
approved by the permit). It would do so
by requiring the description of the
changes in the permit to be sufficiently
detailed to assure compliance with the
required BACT/LAER and monitoring
approaches and to distinguish the
changes from those not authorized to
occur under the approved Green Group.
We are proposing a safeguard, in that
any changes advance approved for a
Green Group relying on a new or
modified control device to meet BACT/
LAER could not be implemented until
the control device meets the BACT/
LAER determination in the permit.
It is within our discretion to remove
Green Groups from 40 CFR 52.21(r)(2),
52.21(j)(4), and 51.166(j)(4) through
rulemaking when doing so better serves
the purposes of the major NSR
program.67 As noted above, the 40 CFR
52.21(r)(2) provisions were established
by EPA in rulemaking to safeguard
against sources tying up increment
consumption rights without making a
substantial financial investment and
against sources inappropriately avoiding
the application of control technology
improvements that might have occurred
since their permit was issued. (See 43
FR 26396, June 19, 1978.) For several
reasons, we do not believe that these
concerns apply to Green Groups as we
are proposing them.
First, at least in the case when a new
or modified air pollution control device
is required, the source under this
proposal must make substantial
financial commitment to comply with
the Green Group designation. This type
of source has every incentive to
complete the construction of the air
pollution control device expeditiously
because, as described above, the
remaining period for the Green Group
qualification is reduced accordingly.
Further, based on our overall pilot
permit experience, sources that wish to
obtain a flexible permit approach are
likely to use it for changes at multiple
emissions activities that could be
constructed over several years. Our
evaluation of the pilot permits found
that the authorized flexibilities were
used extensively and frequent changes
were made.
In addition, once the air pollution
control technology is in operation, we
do not believe significant additional
67 Indeed, as quoted above, 40 CFR 52.21(r)(2)
explicitly provides that ‘‘[t]he Administrator may
extend the 18-month period upon a satisfactory
showing that an extension is justified.’’
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environmental benefits will be gained
by requiring the source to revisit the
BACT or LAER determination for the
changes that are approved as part of the
Green Group, but may not be
constructed for several years. As noted
above, we do not believe that there will
be significant incremental
improvements in state-of-the-art control
technology over a 10-year period.
Moreover, the incentive to be able to
make changes within a Green Group
without further reviews or approvals
can lead sources to employ BACT/LAER
emissions controls when they are not
required to do so, in order to establish
a Green Group.
Finally, we believe that Green Groups
are likely to involve controls that are
state-of-the-art air pollution control
devices since the device must be sized
and designed to accommodate all of the
emissions associated with the emissions
activities that comprise the Green
Group, including the authorized
emissions increase. We believe that the
BACT determination for a Green Group
is likely to be more stringent than BACT
for the individual existing emissions
activities or for the individual
authorized changes alone because it will
likely be more cost effective to control
a larger amount of emissions. The BACT
or LAER selected for the Green Group is
based on the emissions associated with
all of the approved emissions activities,
and the BACT or LAER level must be
achieved (at least in part) through the
use of a common air pollution control
device.
For essentially the same reasons for
removing the applicability of 40 CFR
52.21(r)(2) provisions from Green
Groups activities, we believe that these
activities should be exempted from the
(j)(4) provisions of both 40 CFR 52.21
and 51.166. The (j)(4) provisions
currently require for phased
construction projects that the BACT
determination be reviewed and
modified as appropriate at the latest
reasonable time which occurs no later
than 18 months prior to commencement
of construction of each independent
phase of the project. There again is no
need to evaluate the interdependence of
changes since, under the proposed
Green Group approach, a continuum of
changes is likely over a 10-year period
while a change in the BACT
determination is not.
On the other hand, we do not propose
to exclude the provisions of 40 CFR
52.21(r)(4), 51.166(r)(2), and
51.165(a)(5)(ii) from applying to NSR
permitting actions to establish Green
Group designations. These provisions
subject a source to major NSR upon the
relaxation of certain permit terms that
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had allowed the source to avoid major
NSR. In the designation of a Green
Group, the emissions unit (which could
include an emissions activity to which
an (r)(4) limit was attached) will
undergo major NSR review and be
subject to BACT or LAER. Thus, there
is no need to specifically exempt Green
Groups from the provisions of 40 CFR
52.21(r)(4), 51.166(r)(2), and
51.165(a)(5)(ii) during the life of a Green
Group or after its expiration.
This legal rationale for Green Groups
differs from the legal rationale for Clean
Units, a provision in the 2002 NSR
Improvement rules that the U.S. Court
of Appeals for the D.C. Circuit vacated
in State of New York, et al., v. U.S. EPA,
June 24, 2005, 413 F.3d at 40. As noted
above, an existing stationary source
triggers NSR when it makes a
‘‘modification,’’ which is defined, under
CAA section 111(a)(4), as ‘‘any physical
change. * * * which increases the
amount of any air pollutant emitted’’ by
the source. The EPA based the Clean
Unit provision on the premise that the
source’s construction activities
following permit approval do not
constitute a ‘‘modification’’ under CAA
section 111(a)(4), and therefore do not
trigger application of NSR, even if they
constitute a physical change, as long as
the change does not increase the
source’s permit allowable emissions. We
interpreted the term ‘‘increase[ ]’’
under CAA section 111(a)(4) to
authorize an ‘‘allowables’’
measurement, at least when a source
meets the requirements for Clean Units.
The D.C. Circuit vacated this provision
on grounds that in the context of section
111(a)(4), the plain language meaning of
the term ‘‘increase[ ]’’ refers to actual
emissions, not allowable emissions. In
contrast, this legal rationale for Green
Groups is based on the premise that the
changes and emissions activities that
occur within a Green Group are
specifically authorized to occur as a
result of undergoing, not avoiding,
major NSR. Conversely, other changes
that a source seeks to implement, but
are not authorized in the Green Group,
cannot occur without first obtaining all
necessary preconstruction approvals
that would apply to such changes. The
determination of whether the newly
proposed, but unauthorized changes
trigger NSR would be made using the
‘‘actual-to-projected-actual test’’ upheld
by the D.C. Circuit in 2005.
As noted above, the CAA permit
provisions do not by their terms specify
timing requirements for phased
construction. Current regulations
authorize phased construction activities,
within certain constraints, and those
constructions activities cannot be
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considered to be ‘‘physical change[s]’’
that could amount to a ‘‘modification.’’
This proposal is based on the same legal
rationale, and simply relaxes those
regulatory constraints under certain
circumstances, for the policy reasons
described above.
jlentini on PROD1PC65 with PROPOSALS2
E. What are the conforming regulatory
changes we must make to implement
the Green Group concept?
We are proposing regulatory language
for 40 CFR 51.165, 51.166, and 52.21 to
add Green Group provisions. For Green
Groups, we propose to add new
provisions at 40 CFR 51.165(i),
51.166(z), and 52.21(dd). We are also
proposing to revise 40 CFR 52.21(j)(4)
and (r)(2) and 40 CFR 51.166(j)(4) to
exempt Green Groups from these
provisions.
In addition, for Green Groups, we
propose to amend as necessary the
existing provisions related to netting,
emissions offsets, and determining the
emissions increase that will result from
a proposed project. See this proposed
regulatory language for the full range of
these changes, for example in 40 CFR
52.21(a)(2)(v).
We are also proposing to make
conforming changes to the regulatory
language in appendix S of part 51,
although we have not provided specific
regulatory language in this proposal.
Appendix S contains the permitting
program for major stationary sources in
nonattainment areas lacking an
approved part D NSR program. It
applies for the transition period
between a new nonattainment
designation and our approval of a SIP
revision to implement the
nonattainment NSR requirements (i.e.,
40 CFR 51.165) in the area (see 40 CFR
52.24(k)). We recently revised appendix
S to conform to our December 2002 NSR
regulations (see 72 FR 10367, March 8,
2007). At the same time that we would
finalize the changes to 40 CFR 51.165,
51.166, and 52.21, we intend to finalize
analogous ones in appendix S. Because
the Green Group provisions would be
conforming changes and the public has
the opportunity to review and comment
on the conceptual framework and
regulatory language proposed, we will
not solicit additional comments on
these provisions as they apply in
appendix S.
F. What is an example of how a Green
Group might be used in combination
with a title V permit?
Examples 1 and 2 in section VI.D
described how AOSs and incorporation
of advance approvals in a part 70 permit
could be used to provide flexibility in
certain situations. The following
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example 3 describes how Green Groups
can provide operational flexibility
across applicable requirements through
streamlining.
Example 3: Magnetic Tape Plant With
Multiple Future Changes
This example illustrates a Green
Group and indicates how a source and
permitting authority can streamline
Green Group requirements with other
applicable emissions control
requirements to craft a flexible title V
permit that authorizes a range of
changes at the source while minimizing
the permit terms and conditions
necessary to assure compliance with all
the associated applicable requirements.
In this example, a magnetic tape
manufacturing facility located in an
attainment area consists of two large
production buildings (i.e., Buildings 1
and 2), each with seven magnetic tape
process lines. In particular, the source
has web coating lines used in the
manufacture of magnetic data storage
media as well as equipment for
handling raw materials associated with
coating operations, storage of products
or materials, and power boilers to
support the process activities.
Five of the existing magnetic tape
coating lines in Building 1 are subject to
the MACT standard (part 63, subpart
EE), which requires a 95-percent HAP
emissions reduction from the process
lines and associated solvent storage
tanks, mixing vessels, solvent recovery
equipment, and waste handling devices.
Two of these five lines are also subject
to the NSPS for magnetic tape coating
(part 60, subpart SSS), which requires
up to 95-percent control of VOCs from
coating lines and mixing vessels. The
other two lines are not regulated under
part 60 or part 63 because they are
grandfathered from NSPS subpart SSS
and do not emit any HAP. However,
these two lines are subject to an
emissions limitation under the SIP that
requires an 80-percent reduction in VOC
emissions. For major modifications,
major NSR in this PSD area would
require, for this source, application of
BACT (determined on a case-by-case
basis), along with a determination that
the VOC emissions increase, among
other things, will not cause or
contribute to an exceedance of the
ozone NAAQS or have an adverse
impact on the air quality related values
of any Class I area. The existing storage
tanks are grandfathered from the NSPS
(part 60, subpart Kb), but are subject to
the MACT standard (subpart EE) to the
extent that they store HAP.
The VOC emissions from the
equipment in Building 1 are currently
controlled with a large, very efficient
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(96-percent control) carbon adsorption
system which the source installed at the
time it became subject to MACT subpart
EE. This resulted in voluntary overcontrol of the two lines subject only to
the SIP limitation. The source adopted
this control approach so as to retire the
old control devices that previously
served these two lines and to allow for
flexibility in future operations. With the
voluntary over-control of these two
lines, current total annual VOC
emissions from Building 1 are 500 tpy.
The amount of this over-control would
be approximately 572 tpy, assuming that
the seven lines are equal in their
contributions to the total VOC emissions
of Building 1.
The source would like the flexibility
to make a range of changes within
Building 1, but the exact changes within
this range will depend upon business
conditions during the permit term and,
therefore, are not yet known. Overall,
the source seeks the flexibility to make
the following changes:
• Use new raw materials in coating
solutions or use an entirely new coating
solution;
• Modify the existing process
equipment; and/or
• Add new process equipment of a
similar nature to existing equipment
(including new coating lines) within
this building. This new equipment
would be limited to equipment included
in the definition of ‘‘magnetic tape
manufacturing operation’’ in MACT
subpart EE (40 CFR 63.702).
The source may pursue a two-part
approach to obtain the desired
flexibility to make changes within
Building 1: (1) Obtain a PSD permit that
designates Building 1 as a Green Group
and advance approves the future
changes; and (2) revise the existing title
V permit under the significant
modification process to incorporate all
applicable requirements, as required by
part 70, for the changes that are advance
approved in Building 1 under PSD.
Assuming the source follows this
approach, the source submits a PSD
permit application requesting a Green
Group designation for Building 1. This
permit application must include
descriptions of the types of changes the
source intends to make there over the
next 10 years (as noted above), along
with emissions information associated
with both the changes, especially
regarding any requested increases in
emissions, and the existing operations
of Building 1.
The PSD application must
demonstrate how those changes and the
associated emissions increases in
combination with existing emissions
will comply with PSD requirements for
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Green Groups. In order to meet BACT,
the source in its PSD application
proposes to control emissions from
Building 1, including emissions from
anticipated changes, by (1) Using
permanent total enclosures to capture
all VOC emissions from the building
(including coating lines and associated
mixing vessels, solvent recovery
equipment, and waste handling
devices), and (2) venting these
enclosures and the storage tanks to the
highly efficient (96-percent efficient)
carbon adsorption system currently
used to control emissions from all the
equipment in Building 1. The PSD
application includes the following
BACT-related demonstrations:
• A demonstration that the resultant
96-percent control of VOCs qualifies as
BACT; and
• A demonstration that the existing
carbon adsorption system has the
capacity to maintain 96-percent control
in the face of the increased solvent
loading associated with the anticipated
changes.
In addition, the application contains a
proposed Green Group emissions limit
of 600 tpy VOC and all emissions
information relied upon to calculate this
limit. The proposed limit, in this case,
is the sum of the current baseline actual
emissions for each existing emissions
activity comprising the group (since that
baseline already reflects application of
the proposed BACT), which the source
has calculated to be 500 tpy, plus a 100
tpy emissions increase increment to
accommodate the calculated, maximum
emissions from any future changes for
which the source is seeking approval. In
other cases where current controls do
not reflect application of the proposed
BACT, sources also would be required
to submit actual emissions information
for included activities relative to their
operation before BACT would be
applied. In this example, by subjecting
the coating lines and all of the other
emissions activities in the Green Group
to the BACT level of control, the source
has imposed additional control, not
otherwise required, on the two lines
otherwise subject only to SIP
requirements. While the overall actual
emissions from this group may increase
by 100 tpy upon approval of the Green
Group, the proposed increase would be
subjected to BACT, and overall VOC
emissions would be less by 472 tpy than
the actual emissions level that would
occur for the source were the Green
Group level of control not in effect for
the two lines previously subject to only
to SIP requirements (i.e., 572 tpy overcontrol minus the 100 tpy increase).
The PSD application also includes a
demonstration that a VOC emissions
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increase of 100 tpy from Building 1 will
be consistent with the PSD requirements
applicable to the area. It shows that the
increase, among other things, will not
cause or contribute to ambient ozone in
excess of the ozone NAAQS or have an
adverse impact on the air quality related
values associated with any Class I area.
The application also describes, as
normally required under PSD
permitting, how the source will
demonstrate initial and ongoing
compliance with the BACT emissions
limits. In doing so, the source bears in
mind the requirements of the other
applicable requirements (NSPS subpart
SSS, MACT subpart EE, and the SIP)
with an eye toward streamlining these
requirements, as discussed further
below. For the initial VOC BACT
compliance test, the source proposes to
measure the control efficiency of the
carbon adsorption system by testing at
the inlet and outlet of the system using
EPA Reference Method 25A and to
verify the permanent total enclosures
using EPA Reference Method 204. To
assure ongoing compliance with the
proposed BACT for VOC emissions, the
source proposes to monitor
continuously the Green Group’s single
emissions outlet (the carbon adsorption
system stack) with a CEMS calibrated on
the predominant VOC. (The same CEMS
currently used for compliance purposes
under the existing emissions limits.)
The operating limit for this parameter
(outlet concentration) will be
established during the initial
performance test. This monitoring
system will also serve to assure that the
emissions vented to the carbon adsorber
do not exceed the capacity of the system
(a Green Group requirement), which
would result in an elevated outlet
concentration. In addition, the source
proposes to continuously monitor its
permanent total enclosures using
differential pressure gauges to
demonstrate that these enclosures are at
the prescribed negative pressure relative
to their surroundings. The doors into
the enclosures also are equipped with
contact switches and electronic
interlocks that automatically close the
door after 15 seconds; the actual open
time for each door is monitored and
tracked. An operator alarm sounds if a
door is open longer than 3 minutes.
These types of testing and monitoring
procedures are allowed under NSPS
subpart SSS, MACT subpart EE, and the
SIP as well.
To demonstrate compliance with the
annual VOC emissions limit required for
a Green Group (set, in this case, at the
level of baseline actual emissions at
BACT plus 100 tpy (i.e., 600 tpy VOC)
as projected in the application), the
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source proposes to meet the MRRT
requirements for Green Groups
(discussed previously) by using the
concentration data from the VOC
CERMS on the Building 1 carbon
adsorber outlet coupled with data from
a volumetric flow rate CEMS. Together
these CEMS constitute a continuous
emissions rate monitoring system
(CERMS), which will allow a direct
determination of mass emissions from
this building. Total VOC emissions will
be determined for each month, and the
source will calculate the rolling 12month total for comparison to the
annual VOC emissions limit.
The source also proposes
comprehensive recordkeeping and
reporting in its PSD application. The
proposed recordkeeping includes use of
an automated data acquisition and
handling system (DAHS) to record
CEMS and CERMS readings at least
once every 15 minutes and to make the
necessary calculations.
After review and public comment, the
permitting authority approves the
proposed BACT determination, ambient
air quality analysis, and compliance
assurance measures. The permitting
authority then issues a PSD permit to
the source designating Building 1 as a
Green Group.
This PSD permit provides advance
approval under major NSR for the
described changes within the Green
Group. However, this major NSR
approval does not address the
requirements of the title V permitting
program. Therefore, another step is
needed to enable the source to proceed
with these changes without any further
review or approval by the permitting
authority.
Under the second part of the process
and (in this example) concurrent with
the PSD permit application, the source
submits an application for a significant
permit modification of its part 70
permit. Therein the source proposes to
include the advance approvals under
major NSR in the title V permit so as to
assure compliance with all applicable
requirements relevant to the anticipated
changes. To do so, this application
proposes streamlined requirements to
address the spectrum of changes that
could occur within Building 1 and
includes a streamlining demonstration
and associated documentation.68 In
68 As explained above in section VI.A of this
preamble and footnote 26, in White Paper Number
2 we interpreted our part 70 rules to allow sources
to streamline multiple applicable requirements that
apply to the same emissions unit(s) into a single set
of requirements that assure compliance with all the
subsumed applicable requirements. Sources that
seek to streamline applicable requirements should
submit their request as part of their title V permit
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particular, the application proposes a
streamlined emissions limit of 96percent control of VOC and organic
HAP emissions, to be achieved using the
same control strategy proposed as
BACT. The streamlining demonstration
and documentation show that this 96percent reduction level will assure
compliance with all the emissions limits
that could apply to any of the existing,
modified, or new equipment in Building
1 (i.e., MACT subpart EE, NSPS subpart
SSS, the SIP, and BACT). This
demonstration accounts for the level
and format of the emissions limits (all
in terms of percent reduction), the
associated test methods (all are
consistent), the averaging time (all are
consistent), and the collection of
equipment across which compliance is
demonstrated (all require compliance
for each individual piece of equipment).
The streamlining proposal also
includes streamlined monitoring,
recordkeeping, and reporting
requirements that assure compliance
with the streamlined emissions limit at
least as well as the requirements of the
subsumed applicable requirements. In
this case, the monitoring requirements
associated with the BACT emissions
limit are shown to assure compliance
with the streamlined emissions limit as
least as well as the monitoring
applicable to each less-stringent
emissions limit. Similarly, the
recordkeeping and reporting associated
with the BACT monitoring approach are
appropriate for use with the streamlined
limit and provide no less compliance
assurance than would the recordkeeping
and reporting required for any of the
subsumed monitoring approaches.
In this case, where the PSD
application and streamlining proposal
are being prepared simultaneously, the
source appropriately considered the
other, non-NSR applicable requirements
in its permit application for the BACT
emissions limit and associated MRRT
requirements so that as the BACT limit
(i.e., 96 percent reduction) meshed with
the streamlined requirements in the part
70 permit application. This approach
simplified the streamlining proposal.
The part 70 application essentially
incorporates the description contained
in the PSD permit which established the
Green Group. That is, it describes the
baseline configuration in Building 1, as
well as the types of changes that are
application, identifying the proposed streamlined
requirements and providing a demonstration that
the streamlined requirements assure compliance
with all the underlying, subsumed applicable
requirements. Where the source wishes to
streamline the advance approval under NSR with
all other relevant applicable requirements, the same
title V permit application can address both actions.
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anticipated (mirroring the changes
approved in the Green Group PSD
permit). The part 70 application also
identifies the streamlined requirements
and all the subsumed applicable
requirements implicated by the
potential changes (PSD, NSPS subpart
SSS, MACT subpart EE, and the SIP),
and indicates that PSD authorization
has been received (or is being
concurrently processed). Any physical
or operational changes that implicate
different sets of applicable requirements
would be identified as AOSs, as
discussed previously in Example 2. The
application proposes terms and
conditions to assure compliance with
the streamlined requirements. Focusing
these terms and conditions on the
streamlined requirements simplifies
both the application and the resulting
permit.
The magnitude of the authorized
emissions increase under the proposed
scenario(s) is bounded by the annual
VOC emissions limitation for the Green
Group established at the level of
baseline actual emissions under BACT
plus the 100 tpy VOC emissions
increase approved under PSD. Thus, the
permit application proposes an
aggregate total of 600 tpy VOC. Note that
any VOC emissions within Building 1
will count against this limitation. For
purposes of this example, we have
assumed that no debottlenecking effect
occurs from emissions units that are not
changed themselves. Traditional NSR
(i.e., minor or major NSR, as applicable)
continues to apply outside the Green
Group.
For purposes of the Green Group
(which is a single emissions unit under
the PSD regulations proposed), the
aggregate total emissions figure (600
tpy) included in the part 70 application
fulfills the part 70 requirement that
annual emissions be provided in the
application for each emissions unit.
However, because some of the emissions
activities that are included in the Green
Group are also subject to other
applicable requirements (i.e., the SIP,
NSPS subpart SSS, and/or MACT
subpart EE), they may be considered
emissions units for purposes of these
requirements. As a result, the source
potentially could be required to provide
the annual emissions in tpy for each of
these smaller emissions units in the part
70 permit. Under the part 70 rule
revisions proposed (see proposed 40
CFR 70.5(c)(3)(iii)), for emissions units
that are under an emissions cap, ‘‘tpy
can be reported as part of the aggregate
emissions associated with the cap,
except where more specific information
is needed to determine an applicable
requirement.’’ Thus, because the
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52239
application already stipulates that the
emissions activities are subject to these
other applicable requirements, there is
no need for the source to include annual
emissions for each of the subject
emissions activities.
The source and the permitting
authority then proceed through the
process for a significant permit
modification that involves streamlining
and the incorporation of the Green
Group permit (i.e., the advance approval
issued under major NSR). After review
and public participation, and after
addressing the comments received, the
permitting authority issues a revised
title V permit which includes the
streamlined requirements, the Green
Group permit terms, and a permit
shield.
The source subsequently is able to
make the authorized changes in the
Green Group/Building 1 without
additional review or approval or permit
revisions. Log entries are required if the
source makes changes that cause a shift
to a different AOS. Note that the
notification requirements of the NSPS
and MACT General Provisions continue
to apply if the source adds a new line
or modifies an affected source or facility
within the Green Group.
VIII. What is the effect of these
proposed revisions?
A. If these proposed revisions are
finalized, what are the implications for
approved part 70 programs?
The part 70 regulations provide, in
pertinent part, that—
If part 70 is subsequently revised such that
the Administrator determines that it is
necessary to require a change to an approved
State program, the required revisions to the
program shall be submitted within 12 months
of the final changes to part 70 or within such
other period as authorized by the
Administrator.
See 40 CFR 70.4(a); see also 40 CFR
70.4(i).
The revisions to the part 70 program
proposed build upon the existing
regulatory structure, as promulgated in
1992. For the reasons discussed above,
we believe that these proposed revisions
clarify the existing part 70 regulations.
Our pilot experience—where we worked
closely with several different States—
strongly suggests that these revisions, if
finalized, would likely not necessitate
revisions to many approved State
programs. Based on our pilot
experience, however, we recognize that
State programs differ, and we believe
that at least some States would likely
revise their current part 70 program to
add sufficient authority to implement
the final rule or to make current
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authority on flexible permits more
explicit. We solicit comment on our
initial position that at least some State
programs would require program
revisions in response to the final rule.
We intend to work closely with States
and review expeditiously any
documentation submitted regarding the
adequacy of current part 70 programs
and any proposed program revisions.
Nothing precludes State and local
permitting authorities from issuing
flexible permits, as they may have done
in the past, but they must determine if
sufficient authority exists under their
current operating permit program to do
so. For those States that believe they
lack authority under their current part
70 programs to implement the final rule,
such States should submit proposed
revisions to their title V operating
permits program to their EPA Regional
Offices within 12 months of the date of
publication of the final rule in the
Federal Register. See 40 CFR 70.4(a).
For other States if, based on their
subsequent efforts to implement the
final rule, we determine in writing that
a particular part 70 program does not
provide sufficient authority to
implement the final rule or is
inconsistent with the final rule, then the
relevant State will have 12 months from
the date of our written determination to
submit a proposed operating permit
program consistent with the final rule to
us for review and approval.
B. What are the implications for NSR
programs?
We believe that Green Groups will
have environmental and administrative
benefits like those of PALs.
Accordingly, we propose that the Green
Groups, like PALs, should be a
mandatory program element. When the
Green Group provisions are finalized,
this will require revisions to SIPs or a
demonstration that adequate authority
already exists.
By ‘‘mandatory program element,’’ we
mean that SIPs must include provisions
providing for the issuance of major NSR
permits with Green Group designations.
However, a Green Group would be an
option that a source may, or may not,
choose to seek. In addition, a permitting
authority would have discretion as to
whether or not to issue a Green Group
permit based on the particulars of each
individual case.
Where States and local agencies
would need implementation plan
revisions to be able to issue permits
establishing Green Groups, they must
adopt and submit revisions to their part
51 permitting programs implementing
these minimum program elements no
later than 3 years from the date of
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publication in the Federal Register of
the final Green Group regulations in 40
CFR 51.165 and 51.166. In any area for
which we are the reviewing authority,
or for which we have delegated our
authority to issue permits to State or
local permitting authorities, the changes
would take effect 60 days from the date
of publication in the Federal Register of
the final Green Group regulations in 40
CFR 52.21.
As we noted in the NSR
improvements adopted in 2002, State
and local jurisdictions have significant
freedom to customize their NSR
programs (67 FR 80241). Ever since our
current NSR regulations were adopted
in 1980, we have taken the position that
States may meet the requirements of
part 51 ‘‘with different but equivalent
regulations.’’ See 45 FR 52676.
During the interim period between
this proposal and finalization of the
proposed rules, we believe that certain
major NSR permits with features similar
to a Green Group designation could be
approved under our existing federal
PSD regulations at 40 CFR 52.21. Such
permits would have to abide by the
existing regulations, including the
restrictions at 40 CFR 52.21(r)(2) and
(j)(4), which would differ from this
proposal for Green Groups. Because of
the benefits we believe Green Groups
bring, we invite States to whom we have
delegated the federal PSD program, as
well as States implementing their own
EPA-approved major NSR programs, to
work with us on a case-by-case basis
within the constraints of existing
regulations to determine whether and to
what extent Green Group-like permits
may be available in this interim period.
IX. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order (EO) 12866
(58 FR 51735, October 4, 1993), this
action is a ‘‘significant regulatory
action’’ because it is likely to result in
a rule that may raise novel legal or
policy issues arising out of legal
mandates, the President’s priorities, or
the principles set forth in the Executive
Order. Accordingly, EPA submitted this
action to the Office of Management and
Budget (OMB) for review under EO
12866 and any changes made in
response to OMB recommendations
have been documented in the docket for
this action.
B. Paperwork Reduction Act
This proposed rule would revise
several existing rules. The current
information collection requirements of
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those rules are contained in three
different Information Collection
Requests (ICRs). The Office of
Management and Budget (OMB) has
approved the information collection
requirements for parts 70 and 71 under
the provisions of the Paperwork
Reduction Act, 44 U.S.C. 3501 et seq.
The currently approved ICR for part 70
is assigned ICR number 1587.06 and
OMB number 2060–0243; for part 71,
the ICR number is 1713.05 and the OMB
number is 2060–0336. Similarly, OMB
has approved information collection
requirements for parts 51 and 52 that
govern the State and Federal programs
for preconstruction review and
permitting of major new and modified
sources pursuant to part C (PSD) and
part D (nonattainment major NSR) of
title I of the CAA. The currently
approved ICR for parts 51 and 52 is
assigned ICR number 1230.17 and OMB
number 2060–0003.
The information collection
requirements in this proposed rule have
been submitted for approval to OMB
under the Paperwork Reduction Act, 44
U.S.C. 3501 et seq. The ICR documents
prepared by EPA have been assigned
EPA ICR numbers 1587.08, 1713.07, and
1230.20.
The total economic impact of the
proposed Flexible Air Permitting Rule
over the three-year term of the ICR is
estimated to be $36 million in cost
savings for sources with a burden
reduction of approximately 943,000
labor hours; $19 million in cost savings
for permitting authorities with a burden
reduction of approximately 514,000
labor hours; and costs of $1.4 million
with an increase in burden of
approximately 37,000 labor hours for
EPA.
Burden means the total time, effort, or
financial resources expended by persons
to generate, maintain, retain, or disclose
or provide information to or for a
Federal Agency. This includes the time
needed to: (1) Review instructions; (2)
develop, acquire, install, and utilize
technology and systems for the purposes
of collecting, validating, and verifying
information, processing and
maintaining information, and disclosing
and providing information; (3) adjust
the existing ways to comply with any
previously applicable instructions and
requirements; (4) train personnel to be
able to respond to a collection of
information; (5) search data sources; (6)
complete and review the collection of
information; and (7) transmit or
otherwise disclose the information.
An Agency may not conduct or
sponsor, and a person is not required to
respond to a collection of information
unless it displays a currently valid OMB
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control number. The OMB control
numbers for EPA’s regulations are listed
in 40 CFR part 9 and 48 CFR Chapter
15.
To comment on the Agency’s need for
this information, the accuracy of the
provided burden estimates, and any
suggested methods for minimizing
respondent burden, including the use of
automated collection techniques, EPA
has established a public docket for this
rule, which includes this ICR, under
Docket ID number EPA–HQ–OAR–
2004–0087. Submit any comments
related to the ICR for this proposed rule
to EPA and OMB. See the ADDRESSES
section at the beginning of this notice
for where to submit comments to EPA.
Send comments to OMB at the Office of
Information and Regulatory Affairs,
Office of Management and Budget, 725
17th Street, NW., Washington, DC
20503, Attention: Desk Office for EPA.
Since OMB is required to make a
decision concerning the ICR between 30
and 60 days after September 12, 2007,
a comment to OMB is best assured of
having its full effect if OMB receives it
by October 12, 2007. The final rule will
respond to any OMB or public
comments on the information collection
requirements contained in this proposal.
C. Regulatory Flexibility Act (RFA)
The RFA 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
government jurisdictions.
For purposes of assessing the impacts
of this proposal on small entities, a
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-forprofit enterprise which is independently
owned and operated and is not
dominant in its field.
This proposed rule would merely
clarify existing requirements and allow
regulated entities to seek additional
flexibility for their Clean Air Act
permits, and would not create a new
burden for regulated entities. We have
determined there will be cost savings for
small entities associated with these
proposed revisions. After considering
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the economic impact of this proposed
rule on small entities, I certify that this
action will not have a significant
economic impact on a substantial
number of small entities. Therefore, a
regulatory flexibility analysis is not
required.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Public
Law 104–4, establishes requirements for
Federal agencies to assess the effects of
their regulatory actions on State, local,
and tribal governments and the private
sector. Under section 202 of the UMRA,
2 U.S.C. 1532, we generally must
prepare a written statement, including a
cost-benefit analysis, for any proposed
or final rule that ‘‘includes any Federal
mandate that may result in the
expenditure by State, local, and tribal
governments, in the aggregate, or by the
private sector, of $100 million or more
* * * in any one year.’’ A ‘‘Federal
mandate’’ is defined to include a
‘‘Federal intergovernmental mandate’’
and a ‘‘Federal private sector mandate.’’
2 U.S.C. 658(6). A ‘‘Federal
intergovernmental mandate,’’ in turn, is
defined to include a regulation that
‘‘would impose an enforceable duty
upon State, local, or tribal
governments,’’ 2 U.S.C. 658(5)(A)(i),
except for, among other things, a duty
that is ‘‘a condition of Federal
assistance.’’ 2 U.S.C. 658(5)(A)(i)(I). A
‘‘Federal private sector mandate’’
includes a regulation that ‘‘would
impose an enforceable duty upon the
private sector,’’ with certain exceptions
[2 U.S.C. 658(7)(A)].
Before promulgating a rule for which
a written statement is needed, section
205 of the UMRA generally requires us
to identify and consider a reasonable
number of regulatory alternatives and
adopt the least-costly, most costeffective, or least-burdensome
alternative that achieves the objectives
of the rule. The provisions of section
205 do not apply where they are
inconsistent with applicable law.
Moreover, section 205 allows us to
adopt an alternative other than the leastcostly, most cost-effective, or leastburdensome alternative if the
Administrator publishes with the final
rule an explanation why that alternative
was not adopted. Before we establish
any regulatory requirements that may
significantly or uniquely affect small
governments, including tribal
governments, we must have developed
under section 203 of the UMRA a small
government agency plan. The plan must
provide for notifying potentially
affected small governments, enabling
officials of affected small governments
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52241
to have meaningful and timely input in
the development of our regulatory
proposals with significant Federal
intergovernmental mandates, and
informing, educating, and advising
small governments on compliance with
the regulatory requirements.
We have determined under the
regulatory provisions of title II of the
UMRA that this proposed rule does not
include a Federal mandate that may
result in estimated costs of $100 million
or more to either State, local, or tribal
governments in the aggregate, or to the
private sector. This proposed rule is
estimated to save State, local, and tribal
permitting authorities over $5 million
and to result in an administrative
burden reduction of 135,000 hours.
Thus, this proposed rule is not subject
to the requirements of sections 202 or
205 of the UMRA.
In addition, we have determined that
this proposed rule contains no
regulatory requirements that might
significantly or uniquely affect small
governments. We expect any impact
will act to lower overall administrative
burden to these entities. Therefore, this
proposed rule is not subject to the
requirements of section 203 of the
UMRA.
E. Executive Order 13132: Federalism
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires us to develop an
accountable process to ensure
‘‘meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications.’’ ‘‘Policies that have
federalism implications’’ is defined in
the Executive Order to include
regulations that have ‘‘substantial direct
effects on the States, or on the
distribution of power and
responsibilities among the various
levels of government.’’
This proposal 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 proposal
should result in cost savings and
administrative burden reductions for
States and will not alter the overall
relationship or distribution of powers
between governments for the part 70
and part 71 operating permits programs
or for the part 51 and part 51 NSR
programs. Thus, Executive Order 13132
does not apply to this proposed rule.
In the spirit of Executive Order 13132,
and consistent with our policy to
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promote communication between us
and State and local governments, we
specifically solicit comment on this
proposed rule from State and local
officials.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, ‘‘Consultation
and Coordination with Indian Tribal
Governments’’ (65 FR 67249, November
6, 2000), requires us to develop an
accountable process to ensure
‘‘meaningful and timely input by tribal
officials in the development of
regulatory policies that have tribal
implications.’’ ‘‘Policies that have tribal
implications’’ is defined in the
Executive Order to include regulations
that have ‘‘substantial direct effects on
one or more Indian tribes, on the
relationship between the Federal
government and the Indian tribes, or on
the distribution of power and
responsibilities between the Federal
government and Indian tribes.’’
These proposed rule revisions do not
have tribal implications because they
will not have a substantial direct effect
on one or more Indian tribes, on the
relationship between the Federal
government and Indian tribes, or on the
distribution of power and
responsibilities between the Federal
government and Indian tribes, as
specified in Executive Order 13175.
This action does not significantly or
uniquely affect the communities of
Indian tribal governments. Accordingly,
the requirements of Executive Order
13175 do not apply to these proposed
rule revisions. We solicit comments
from Indian tribal governments on the
proposed rule.
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G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
This proposed rule is not subject to
the Executive Order because it is not
economically significant as defined in
Executive Order 12866, and because the
Agency does not have reason to believe
the environmental health or safety risks
addressed by this action present a
disproportionate risk to children
because it does not establish an
environmental standard intended to
mitigate health or safety risks.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This rule is not subject to Executive
Order 13211, ‘‘Actions Concerning
Regulations That Significantly Affect
Energy Supply, Distribution, or Use’’ (66
FR 28355, May 22, 2001) because it is
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not a significant regulatory action under
Executive Order 12866.
This proposed rule is not a
‘‘significant energy action,’’ as defined
in Executive Order 13211, because it is
not likely to have a significant adverse
effect on the supply, distribution, or use
of energy. As noted earlier, this action
would simply clarify existing
requirements and would not impose any
new requirements, and thus would not
affect the supply, distribution, or use of
energy.
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, directs us to use voluntary
consensus standards in its regulatory
activities unless to do so would be
inconsistent 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 bodies.
The NTTAA directs us to provide
Congress, through OMB, explanations
when the Agency decides not to use
available and applicable voluntary
consensus standards.
The NTTAA does not apply to this
proposed rule because it does not
involve technical standards. Therefore,
we did not consider the use of any
voluntary consensus standards.
List of Subjects
40 CFR Part 51
Environmental protection,
Administrative practice and procedures,
Air pollution control, Intergovernmental
relations, Reporting and recordkeeping
requirements.
40 CFR Part 52
Environmental protection,
Administrative practice and procedures,
Air pollution control, Intergovernmental
relations, Reporting and recordkeeping
requirements.
40 CFR Part 70
Environmental protection,
Administrative practice and procedures,
Air pollution control, Intergovernmental
relations, Reporting and recordkeeping
requirements.
40 CFR Part 71
Environmental protection,
Administrative practice and procedures,
Air pollution control, Intergovernmental
relations, Reporting and recordkeeping
requirements.
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Dated: August 28, 2007.
Stephen L. Johnson,
Administrator.
For the reasons set out in the
preamble, title 40, chapter I of the Code
of Federal Regulations is proposed to be
amended as set forth below.
PART 51—[AMENDED]
1. The authority citation for part 51
continues to read as follows:
Authority: 23 U.S.C. 101; 42 U.S.C. 7401–
7671q.
Subpart I—[Amended]
2. Section 51.165 is amended as
follows:
a. By adding paragraph (a)(1)(v)(G);
b. By revising paragraph (a)(1)(xii)(A);
c. By revising paragraph
(a)(1)(xxxv)(D);
d. By revising paragraph (a)(2)(ii)(A);
e. By adding paragraph (a)(2)(v);
f. By revising paragraph (a)(6)
introductory text; and
g. By adding paragraph (i).
The additions and revisions read as
follows:
§ 51.165
Permit requirements.
(a) * * *
(1) * * *
(v) * * *
(G) This definition shall not apply to
approved physical changes or changes
in the method of operation within a
Green Group with respect to any Green
Group pollutant when the major
stationary source is complying with the
requirements under paragraph (i) of this
section for a Green Group for that
pollutant.
*
*
*
*
*
(xii)(A) Actual emissions means the
actual rate of emissions of a regulated
NSR pollutant from an emissions unit,
as determined in accordance with
paragraphs (a)(1)(xii)(B) through (D) of
this section, except that this definition
shall not apply for calculating whether
a significant emissions increase has
occurred, or for establishing a PAL
under paragraph (f) of this section or a
Green Group under paragraph (i) of this
section. Instead, paragraphs
(a)(1)(xxviii) and (xxxv) of this section
shall apply for those purposes.
*
*
*
*
*
(xxxv) * * *
(D) For a PAL or Green Group for a
major stationary source, the baseline
actual emissions shall be calculated for
existing electric utility steam generating
units in accordance with the procedures
contained in paragraph (a)(1)(xxxv)(A)
of this section, for other existing
emissions units in accordance with the
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procedures contained in paragraph
(a)(1)(xxxv)(B) of this section, and for a
new emissions unit in accordance with
the procedures contained in paragraph
(a)(1)(xxxv)(C) of this section.
*
*
*
*
*
(2) * * *
(ii) * * *
(A) Except as otherwise provided in
paragraphs (a)(2)(iii) through (v) of this
section, and consistent with the
definition of major modification
contained in paragraph (a)(1)(v)(A) of
this section, a project is a major
modification for a regulated NSR
pollutant if it causes two types of
emissions increases—a significant
emissions increase (as defined in
paragraph (a)(1)(xxvii) of this section),
and a significant net emissions increase
(as defined in paragraphs (a)(1)(vi) and
(x) of this section). The project is not a
major modification if it does not cause
a significant emissions increase. If the
project causes a significant emissions
increase, then the project is a major
modification only if it also results in a
significant net emissions increase.
*
*
*
*
*
(v) The plan shall require that for any
major stationary source with a Green
Group for a regulated NSR pollutant, the
owner or operator shall comply with the
requirements in paragraph (i) of this
section for those emissions activities
included within the Green Group.
*
*
*
*
*
(6) Each plan shall provide that the
following specific provisions apply to
projects at existing emissions units at a
major stationary source (other than
projects at a Green Group or at a source
with a PAL) in circumstances where
there is a reasonable possibility that a
project that is not a part of a major
modification may result in a significant
emissions increase and the owner or
operator elects to use the method
specified in paragraphs
(a)(1)(xxviii)(B)(1) through (3) of this
section for calculating projected actual
emissions. Deviations from these
provisions will be approved only if the
State specifically demonstrates that the
submitted provisions are more stringent
than or at least as stringent in all
respects as the corresponding provisions
in paragraphs (a)(6)(i) through (v) of this
section.
*
*
*
*
*
(i) Green Groups. The plan shall
provide for Green Groups according to
the provisions in paragraphs (i)(1)
through (17) of this section.
(1) Applicability. The reviewing
authority may issue a permit under
regulations approved pursuant to this
section designating a Green Group at
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any existing major stationary source if
the permit contains terms and
conditions assuring that the Green
Group meets the requirements in
paragraphs (i)(1) through (17) of this
section.
(i) Changes at a Green Group. Any
physical change in or change in the
method of operation authorized for a
Green Group pursuant to the
requirements in paragraphs (i)(1)
through (17) of this section that
maintains the Green Group’s total
emissions at or below the Green Group
emissions limit and maintains the Green
Group’s compliance with its LAER
limit(s):
(A) Is not a major modification for the
Green Group pollutant; and
(B) Does not have to be approved
through the plan’s nonattainment major
NSR program.
(ii) Prior requirements. A major
stationary source shall continue to
comply with all remaining applicable
Federal or State requirements, emissions
limitations, and work practice
requirements that were established prior
to the effective date of the Green Group.
(2) Definitions. The plan shall use the
definitions in paragraphs (i)(2)(i)
through (iv) of this section for the
purpose of developing and
implementing regulations that authorize
the use of Green Groups consistent with
paragraphs (i)(1) through (17) of this
section. When a term is not defined in
these paragraphs, it shall have the
meaning given in paragraph (a)(1) or (f)
of this section or in the Act.
(i) Green Group means a group of new
and/or existing emissions activities that
is characterized by use of a common,
dedicated air pollution control device
and that has been designated as a Green
Group by the reviewing authority in a
permit issued under regulations
approved pursuant to this section. A
Green Group is a single emissions unit
for purposes of this section.
(ii) Green Group pollutant means a
pollutant emitted from the emissions
activities that comprise the Green Group
and for which a Green Group is
designated at a major stationary source.
(iii) Green Group permit means the
major NSR permit issued by the
reviewing authority that establishes a
Green Group for a major stationary
source.
(iv) Green Group emissions limit
means an emissions limitation for the
Green Group pollutant, expressed in
tons per year, that is enforceable as a
practical matter and established for a
Green Group at a major stationary
source in accordance with paragraphs
(i)(1) through (17) of this section.
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(3) Permit application requirements.
The owner or operator of a major
stationary source must request approval
for a Green Group in an application for
a major NSR permit that meets the
requirements of this section, as
applicable, and of sections 172(c)(5) and
173 of the Act. As part of a permit
application requesting a Green Group,
the owner or operator of a major
stationary source shall submit the
following information to the reviewing
authority for approval:
(i) List of designated emissions
activities. A list of the emissions
activities proposed for inclusion in the
Green Group. In addition, the owner or
operator of the source shall indicate
which, if any, Federal or State
applicable requirements, emissions
limitations, or work practices apply to
each activity.
(ii) Baseline actual emissions.
Calculations of the baseline actual
emissions from included emissions
activities (with supporting
documentation). Baseline actual
emissions are to include emissions
associated not only with operation of
the activity, but also emissions
associated with startup, shutdown, and
malfunction.
(iii) Monitoring data conversion
procedures. The calculation procedures
that the major stationary source owner
or operator proposes to use to convert
the monitoring system data to monthly
emissions and annual emissions based
on a 12-month rolling total for each
month as required by paragraph
(i)(15)(i) of this section.
(iv) Description. A description of the
equipment that comprises the Green
Group, including a description of
existing emissions activities, proposed
physical changes or changes in method
of operation (which may include the
addition of new emissions activities),
and the common air pollution control
device. The description must provide
information about maximum total
emissions that will be generated by the
Green Group’s emissions activities and
the associated characteristics of the
combined emissions streams (including
the worst-case emissions stream) that
will be ducted to the common air
pollution control device. The
description must be sufficient:
(A) To allow the reviewing authority
to distinguish changes proposed to be
authorized in the Green Group from
unauthorized changes; and
(B) To enable the reviewing authority
to determine LAER for the Green Group
consistent with paragraphs (i)(4)(ii) and
(i)(7)(v) of this section.
(v) Control technology demonstration.
A demonstration that the proposed
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control technology represents LAER.
Such a demonstration shall confirm that
the emissions reduction capacity of the
proposed common control device is
sufficient to meet the relevant emissions
reduction requirement, considering the
maximum total emissions from the
Green Group and the associated
characteristics of the combined
emissions streams that will be ducted to
the common air pollution control
device. The LAER demonstration shall
be based on worst-case emissions from
the new and existing emissions
activities authorized for the Green
Group.
(vi) Monitoring system. A proposed
monitoring system sufficient to meet the
requirements of paragraph (i)(13) of this
section with respect to Green Group
emissions limit(s) and the requirements
of paragraph (i)(14) of this section with
respect to LAER-related limitations.
(vii) Proposed Green Group emissions
limit. The proposed Green Group
emissions limit, in tons per year, with
supporting documentation including,
but not limited to, the following:
(A) Baseline actual emissions of
existing emissions activities proposed to
be included in the Green Group,
adjusted to reflect the application of
LAER; and
(B) The amount of emissions growth
proposed for the Green Group as the
result of the proposed physical,
operational, and other changes.
(4) General requirements for
designating a Green Group. The plan
shall provide that the reviewing
authority may designate a Green Group
at an existing major stationary source
through issuance of a nonattainment
major NSR permit under regulations
approved pursuant to this section,
provided that in addition the
requirements in paragraphs (i)(4)(i)
through (vii) of this section are met.
(i) Green Group emissions limit. The
reviewing authority, consistent with
regulations approved pursuant to
paragraph (i)(6) of this section, shall
establish a Green Group emissions limit
in tons per year for those emissions
activities included under the Green
Group (including any new emissions
activities added within the Green
Group). For each month during the
Green Group effective period after the
first 12 months of establishing the Green
Group, the major stationary source
owner or operator shall show that the
sum of the monthly emissions from each
included emissions activity for the
previous 12 consecutive months is less
than or equal to the Green Group
emissions limit (i.e., a 12-month total,
rolled monthly). For each month during
the first 11 months from the Green
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Group effective date, the major
stationary source owner or operator
shall show that the sum of the preceding
monthly emissions from the Green
Group effective date for each emissions
activity under the Green Group is less
than or equal to the Green Group
emissions limit.
(ii) LAER emissions limit. The
reviewing authority shall determine
LAER for the emissions of the Green
Group pollutant from the group of
emissions activities designated as a
Green Group. The LAER emissions limit
shall ensure that the emissions of the
emissions activities included in the
Green Group are ducted to a common,
dedicated air pollution control device.
The control device, in combination with
any additional control measures
consistent with paragraphs (i)(4)(ii)(A)
and (B) of this section, must achieve the
LAER level of emissions reductions for
the Green Group pollutant.
(A) In addition to the requirement to
duct emissions from the Green Group to
a common air pollution control device,
additional control measures such as
pollution prevention (as defined under
paragraph (a)(1)(xxvi) of this section),
work practices, and/or operational
standards may be defined as part of the
approved control measures.
(B) Pollution prevention measures
that have been determined to represent
LAER may be approved to apply during
certain periods of operation. The
included emissions activities must have
ductwork extending to the common air
pollution control device, but the owner
or operator would be allowed to bypass
the control device during periods when
the pollution prevention alternative is
in use, consistent with the LAER
determination. Emissions activities that
exclusively use the pollution prevention
alternative and never use the common
air pollution control device may not be
included in the Green Group.
(iii) Permit content. The Green Group
permit shall contain all the
requirements of paragraph (i)(7) of this
section.
(iv) Included emissions. The Green
Group emissions limit shall include
fugitive emissions of the Green Group
pollutant, to the extent quantifiable,
from all emissions activities included
under the Green Group.
(v) Regulated pollutant. Each Green
Group shall regulate emissions of only
one pollutant. However, the same
collection of emissions activities may be
designated separately as a Green Group
for another pollutant.
(vi) Effective period. Each Green
Group designation shall have an
effective period of 10 years.
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(vii) Monitoring, recordkeeping, and
reporting. The Green Group permit shall
require the owner or operator to comply
with the monitoring, recordkeeping, and
reporting requirements in paragraphs
(i)(13) through (16) of this section for
each included emissions activity.
(5) General provisions for Green
Groups. The plan shall require that the
provisions set out in paragraphs (i)(5)(i)
through (iv) of this section apply to
Green Groups:
(i) Any project for which the owner or
operator begins actual construction after
the effective date of a Green Group
designation and before its expiration
date will be considered to have occurred
while the emissions unit was a Green
Group.
(ii) At no time (during or after the
Green Group effective period) are
emissions reductions of a Green Group
pollutant that occur during the Green
Group effective period creditable as
decreases for purposes of offsets under
paragraph (a)(3)(ii) of this section unless
the Green Group emissions limit is
reduced by the amount of such
emissions reductions and such
reductions would be creditable in the
absence of the Green Group designation.
No emissions reduction credit can be
generated for emissions growth that was
authorized under the Green Group
permit, but never realized.
(iii) At no time (during or after the
Green Group effective period) are
emissions increases or reductions of a
Green Group pollutant that occur during
the Green Group effective period
creditable for purposes of calculating a
net emissions increase under paragraph
(a)(1)(vi) of this section (that is, must
not be used in a ‘‘netting analysis’’),
unless the Green Group emissions limit
is reduced by the amount of such
emissions reductions and such
reductions would be creditable in the
absence of the Green Group designation.
No emissions reduction credit can be
generated for emissions growth that was
authorized under the Green Group
permit, but never realized.
(iv) The Green Group designation of
an emissions unit is not affected by
redesignation of the attainment status of
the area in which it is located. That is,
if a Green Group is located in an
attainment area and the area is
redesignated to nonattainment, its Green
Group designation is not affected.
Similarly, redesignation from
nonattainment to attainment does not
affect the Green Group designation.
However, if an existing Green Group
designation expires, it must re-qualify
under the requirements that are
currently applicable in the area.
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(6) Setting the 10-year Green Group
emissions limit. The plan shall provide
that the Green Group emissions limit is
to be established as follows:
(i) Except as provided in paragraphs
(i)(6)(ii) through (iv) of this section, the
Green Group emissions limit shall be
established as the sum of the baseline
actual emissions (as defined in
paragraph (a)(1)(xxxv) of this section) of
the Green Group pollutant for each
emissions activity included in the Green
Group. When establishing the Green
Group emissions limit, for a Green
Group pollutant, a single period of 24
consecutive months must be used to
determine the baseline actual emissions
for all existing emissions activities.
However, a different period of 24
consecutive months may be used for
each different Green Group pollutant.
Emissions associated with activities that
were permanently shut down after this
24-month period must be subtracted
from the Green Group emissions limit.
The reviewing authority shall specify a
reduced Green Group emissions limit(s)
(in tons/yr) in the Green Group permit
to become effective on the future
compliance date(s) of any applicable
Federal or State regulatory
requirement(s) that the reviewing
authority is aware of prior to issuance
of the Green Group permit.
(ii) For activities (which do not
include modifications to existing units)
on which actual construction began
after the 24-month period, in lieu of
adding the baseline actual emissions as
specified in paragraph (i)(6)(i) of this
section, the emissions must be added to
the Green Group emissions limit in an
amount equal to the potential to emit of
the activities.
(iii) The reviewing authority shall
establish the Green Group emissions
level by adjusting the total derived
according to paragraphs (i)(6)(i) and (ii)
of this section to reflect:
(A) The application of LAER; and
(B) An additional amount of actual
emissions consistent with the growth
approved for the Green Group.
(7) Content of the Green Group
permit. The plan shall require that the
Green Group permit contain the
elements listed in paragraphs (i)(7)(i)
through (xiii) of this section and any
other provisions that the reviewing
authority deems necessary to implement
the Green Group.
(i) The Green Group pollutant.
(ii) A description of the equipment
that comprises the Green Group,
including a description of existing
emissions activities, any authorized
physical changes or changes in method
of operation, and the common air
pollution control device. The
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description must provide information
about the maximum total emissions that
will be generated by the Green Group’s
emissions activities and the associated
characteristics of the combined
emissions streams that will be ducted to
the common air pollution control
device. The description must be
sufficient to distinguish, when a change
is subsequently made in the Green
Group, whether that change was
authorized under the Green Group
permit.
(iii) A statement designating the
described equipment as a Green Group.
(iv) The Green Group emissions limit
(in terms of a 12-month total, rolled
monthly) for the group of emissions
activities included under the Green
Group.
(v) All emissions limitations and work
practice requirements established to
ensure that LAER is met.
(vi) The Green Group effective date
and the expiration date of the Green
Group (i.e., the Green Group effective
period). If the source owner or operator
must construct a new air pollution
control device or modify an existing
device as a result of the LAER
determination for the Green Group, the
permit may provide that the existing
emissions activities within the Green
Group are not required to meet the
LAER emissions limitation(s) or the
Green Group emissions limit until the
new or modified air pollution control
device is in operation. (That is, such
emissions activities may continue to
meet pre-existing emissions limitations
until that time.) However, new and
modified emissions activities within the
Green Group must be subject to LAER
upon startup. In addition, the Green
Group must be subject to the Green
Group emissions limit (and associated
monitoring, recordkeeping, and
reporting requirements) beginning at the
time that the new or modified air
pollution control device is placed in
operation.
(vii) Specification in the Green Group
permit that if a major stationary source
owner or operator applies to renew a
Green Group in accordance with
paragraph (i)(11) of this section before
the end of the effective period, then the
Green Group shall not expire at the end
of the effective period. It shall remain in
effect until a new Green Group permit
is issued by the reviewing authority.
(viii) A requirement that emissions
calculations for compliance purposes
must include emissions from startups,
shutdowns, and malfunctions.
(ix) A requirement that, once the
Green Group expires, the major
stationary source is subject to the
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requirements of paragraph (i)(10) of this
section.
(x) The calculation procedures that
the major stationary source owner or
operator shall use to convert the
monitoring system data to monthly
emissions and annual emissions based
on a 12-month rolling total as required
by paragraph (i)(15)(i) of this section.
(xi) A requirement that the major
stationary source owner or operator
meet all applicable requirements for
monitoring, testing, and operation in
accordance with the provisions of
paragraphs (i)(13) and (14) of this
section.
(xii) A requirement to retain the
records required under paragraph (i)(15)
of this section on site. Such records may
be retained in an electronic format.
(xiii) A requirement to submit the
reports required under paragraph (i)(16)
of this section by the required
deadlines.
(8) Green Group effective period. The
plan shall require that the reviewing
authority specify an effective period of
10 years. The effective period begins
upon the Green Group effective date,
which is the date that the Green Group
permit becomes effective.
(9) Reopening of the Green Group
permit. The plan shall provide that the
requirements in paragraphs (i)(9)(i)
through (iii) of this section apply to
reopening Green Group permits.
(i) Mandatory reopenings. During the
Green Group effective period, the
reviewing authority must reopen the
Green Group permit to:
(A) Correct typographical/calculation
errors made in setting the Green Group
emissions limit or reflect a more
accurate determination of emissions
used to establish this limit;
(B) Reduce the Green Group
emissions limit if the owner or operator
of the major stationary source creates
creditable emissions reductions for use
as offsets under paragraph (a)(3)(ii) of
this section; and
(C) Reduce the Green Group
emissions limit if the owner or operator
of the major stationary source creates
creditable emissions reductions for use
in a netting analysis under paragraph
(a)(1)(vi) of this section.
(ii) Discretionary reopenings. The
reviewing authority shall have
discretion to reopen the Green Group
permit for the purposes listed in
paragraphs (i)(9)(ii)(A) through (C) of
this section. If the reviewing authority
declines to reopen the Green Group
permit for any of these purposes, the
Green Group emissions limit must be
adjusted upon expiration of the Green
Group designation or upon renewal of
the source’s title V permit, whichever
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comes first. The major stationary source
owner or operator is responsible for
compliance with any new applicable
requirements, regardless of when the
permit is reopened and adjusted.
(A) To reduce the Green Group
emissions limit to reflect newly
applicable Federal requirements (for
example, NSPS) with compliance dates
after the Green Group effective date;
(B) To reduce the emissions limit
consistent with any other requirement,
that is enforceable as a practical matter,
and that the State may impose on the
major stationary source under the State
Implementation Plan; and
(C) To reduce the emissions limit if
the reviewing authority determines that
a reduction is necessary to avoid
causing or contributing to a NAAQS or
PSD increment violation, or to an
adverse impact on an air quality related
value that has been identified for a
Federal Class I area by a Federal Land
Manager and for which information is
available to the general public.
(iii) Required process. Except for the
permit reopening in paragraph
(i)(9)(i)(A) of this section for the
correction of typographical/calculation
errors that do not increase the Green
Group emissions limit, all other
reopenings shall be carried out in
accordance with the full public
participation requirements for major
NSR permitting under the regulations
approved pursuant to this section.
(10) Expiration of a Green Group. The
plan shall require that any Green Group
designation that is not renewed in
accordance with the procedures in
paragraph (i)(11) of this section shall
expire at the end of its effective period.
After expiration of the Green Group
designation, the following provisions
apply:
(i) The emissions unit defined by the
Green Group remains an emissions unit
for purposes of major NSR and remains
subject to the LAER control
requirements; Green Group emissions
limit; any shorter-term emissions limits;
and monitoring, recordkeeping,
reporting, and testing requirements
imposed by the Green Group permit.
(ii) The major stationary source owner
or operator shall continue to comply
with any State or Federal applicable
requirements (LAER, RACT, NSPS, etc.)
that may have applied either during or
prior to the Green Group effective
period.
(iii) Any subsequent physical change
or change in the method of operation at
the emissions unit defined by the Green
Group will be subject to nonattainment
major NSR requirements if such change
meets the definition of major
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modification in paragraph (a)(1)(v) of
this section.
(11) Renewal of a Green Group. The
plan shall require that the following
provisions apply to renewal of a Green
Group:
(i) Required procedures. A Green
Group may be renewed through
issuance of a new major NSR permit
according to all the requirements of this
paragraph (i) for the initial Green Group
designation.
(ii) Application deadline. A major
stationary source owner or operator
shall submit a timely application to the
reviewing authority to request renewal
of a Green Group. A timely application
is one that is submitted at least 6
months prior to, but not earlier than 18
months from, the date that the Green
Group designation would otherwise
expire. This deadline for application
submittal is to ensure that the Green
Group designation will not expire before
the Green Group is renewed. If the
owner or operator of a major stationary
source submits a complete application
to renew the Green Group within this
time period, then the Green Group shall
continue to be effective until the new
nonattainment major NSR permit with
the renewed Green Group is issued.
(12) Increasing a Green Group
emissions limit during its effective
period. The plan shall provide that the
reviewing authority may increase a
Green Group emissions limit during its
effective period only if the increase is
contained in a new permit incorporating
the increase into a new Green Group
consistent with the requirements of the
regulations approved pursuant to this
section.
(13) Monitoring requirements for
Green Group emissions limitations. The
plan shall provide that the following
monitoring requirements apply to Green
Groups.
(i) General requirements.
(A) Each Green Group permit must
contain enforceable requirements for the
monitoring system that accurately
determines, in terms of mass per unit of
time, emissions of the Green Group
pollutant from the emissions activities
under the Green Group. Any monitoring
system authorized for use in the Green
Group permit must be based on sound
science and meet generally acceptable
scientific procedures for data quality
and manipulation. Additionally, the
information generated by such system
must meet minimum legal requirements
for admissibility in a judicial
proceeding to enforce the Green Group
permit.
(B) The Green Group monitoring
system must employ one or more of the
four general monitoring approaches
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meeting the minimum requirements set
forth in paragraphs (i)(13)(ii)(A) through
(D) of this section and must be approved
by the reviewing authority.
(C) Notwithstanding paragraph
(i)(13)(i)(B) of this section, you may also
employ an alternative monitoring
approach that meets paragraph
(i)(13)(i)(A) of this section if approved
by the reviewing authority.
(D) Failure to use a monitoring system
that meets the requirements of this
section renders the Green Group
invalid.
(ii) Minimum performance
requirements for approved monitoring
approaches. The following are
acceptable general monitoring
approaches when conducted in
accordance with the minimum
requirements in paragraphs (i)(13)(iii)
through (ix) of this section:
(A) Mass balance calculations for
activities using coatings or solvents;
(B) CEMS;
(C) CPMS or PEMS; and
(D) Emissions factors.
(iii) Mass balance calculations. An
owner or operator using mass balance
calculations to monitor the Green Group
pollutant emissions from activities
using coating or solvents shall meet the
following requirements:
(A) Provide a demonstrated means of
validating the published content of the
Green Group pollutant that is contained
in or created by all materials used in or
at the emissions activity;
(B) Assume that the emissions activity
emits all of the Green Group pollutant
that is contained in or created by any
raw material or fuel used in or at the
emissions activity, if it cannot otherwise
be accounted for in the process; and
(C) Where the vendor of a material or
fuel, which is used in or at the
emissions activity, publishes a range of
pollutant content from such material,
the owner or operator must use the
highest value of the range to calculate
the Green Group pollutant emissions
unless the reviewing authority
determines there is site-specific data or
a site-specific monitoring program to
support another content within the
range.
(iv) CEMS. An owner or operator
using CEMS to monitor Green Group
pollutant emissions shall meet the
following requirements:
(A) CEMS must comply with
applicable Performance Specifications
found in 40 CFR part 60, appendix B;
and
(B) CEMS must sample, analyze, and
record data at least every 15 minutes
while the emissions activity is
operating.
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(v) CPMS or PEMS. An owner or
operator using CPMS or PEMS to
monitor Green Group pollutant
emissions shall meet the following
requirements:
(A) The CPMS or the PEMS must be
based on current site-specific data
demonstrating a correlation between the
monitored parameter(s) and the Green
Group pollutant emissions across the
range of operation of the emissions
activity; and
(B) Each CPMS or PEMS must sample,
analyze, and record data at least every
15 minutes, or at another less frequent
interval approved by the reviewing
authority, while the emissions activity
is operating.
(vi) Emissions factors. An owner or
operator using emissions factors to
monitor Green Group pollutant
emissions shall meet the following
requirements:
(A) All emissions factors shall be
adjusted, if appropriate, to account for
the degree of uncertainty or limitations
in the factors’ development;
(B) The emissions activity shall
operate within the designated range of
use for the emissions factor, if
applicable; and
(C) If technically practicable, the
owner or operator of a significant or
major emissions activity that relies on
an emissions factor to calculate Green
Group pollutant emissions shall
conduct validation through performance
testing or other scientifically valid
means approved by the reviewing
authority to determine a site-specific
emissions factor. Such testing or other
means shall occur within 6 months of
Green Group permit issuance.
(vii) Missing data procedures. A
source owner or operator must record
and report maximum potential
emissions without considering
enforceable emissions limitations or
operational restrictions for an emissions
activity during any period of time that
there is no monitoring data, unless
another method for determining
emissions during such periods is
specified in the Green Group permit.
(viii) Alternative requirements.
Notwithstanding the requirements in
paragraphs (i)(13)(iii) through (vii) of
this section, where an owner or operator
of an emissions activity cannot
demonstrate a correlation between the
monitored parameter(s) and the Green
Group pollutant emissions rate at all
operating points of the emissions
activity, the reviewing authority shall, at
the time of permit issuance:
(A) Establish default value(s) for
determining compliance with the Green
Group emissions limit based on the
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highest potential emissions reasonably
estimated at such operating point(s); or
(B) Determine that operation of the
emissions activity during operating
conditions when there is no correlation
between monitored parameter(s) and the
Green Group pollutant emissions is a
violation of the Green Group emissions
limit.
(ix) Re-validation. All data used to
establish the Green Group pollutant
emissions must be re-validated through
performance testing or other
scientifically valid means approved by
the reviewing authority. Such testing
must occur at least once every 5 years
after issuance of the Green Group.
(14) Additional monitoring
requirements for LAER. The plan shall
provide that the permit must also
require the owner or operator with a
Green Group to monitor, measure, and
record data sufficient to determine
whether:
(i) The emissions reduction measures
(including the Green Group air
pollution control device) meet the
emissions limitations and/or work
practice requirements adopted in
conjunction with LAER; and
(ii) The demonstrated capacity of the
Green Group air pollution control
device was exceeded by the emissions
stream(s) directed to it at any time
during the reporting period. The
capacity of the control device is
considered exceeded if the
characteristics of the emissions stream
entering the device are outside the range
for which it has been demonstrated that
the device can achieve LAER, absent
valid monitoring data (from a
continuous monitoring system or other
monitoring approach approved for such
use by the reviewing authority) showing
compliance with LAER at the new
operating level. A period of exceedance
is considered a deviation for purposes of
recordkeeping and reporting.
(15) Recordkeeping requirements. The
plan shall require that the following
recordkeeping requirements apply to
Green Groups:
(i) Records to determine compliance.
The Green Group permit shall require
an owner or operator to retain a copy of
all records necessary to determine
compliance with any requirement of
paragraph (i) of this section and of the
Green Group permit, including a
determination of each emissions
activity’s 12-month rolling total
emissions, for 5 years from the date of
such record.
(ii) Other records. The Green Group
permit shall require an owner or
operator to retain a copy of the
following records for the duration of the
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Green Group effective period plus 5
years:
(A) A copy of the Green Group permit
application and any applications for
revisions to the Green Group permit;
and
(B) Each annual certification of
compliance pursuant to title V and the
data relied on in certifying the
compliance.
(16) Reporting and notification
requirements. The plan shall require the
owner or operator to submit semiannual monitoring reports and prompt
deviation reports to the reviewing
authority in accordance with the
applicable title V operating permit
program. The reports shall meet the
requirements in paragraphs (i)(16)(i)
through (iii) of this section.
(i) Semi-annual report. The semiannual report shall be submitted to the
reviewing authority within 30 days of
the end of each reporting period. This
report shall contain the information
required in paragraphs (i)(16)(i)(A)
through (G) of this section.
(A) The identification of owner and
operator and the permit number.
(B) Total annual emissions (tons per
year) from the emissions activities
included under the Green Group, based
on a 12-month rolling total for each
month in the reporting period recorded
pursuant to paragraph (i)(15)(i) of this
section.
(C) All data relied upon, including,
but not limited to, any Quality
Assurance or Quality Control data, in
calculating the monthly and annual
Green Group pollutant emissions.
(D) A list of any emissions activities
included under the Green Group that
were added during the preceding 6month period.
(E) The number, duration, and cause
of any deviations or monitoring
malfunctions (other than the time
associated with zero and span
calibration checks), and any corrective
action taken.
(F) A notification of a shutdown of
any monitoring system, whether the
shutdown was permanent or temporary,
the reason for the shutdown, the
anticipated date that the monitoring
system will be fully operational or
replaced with another monitoring
system, and whether the emissions
activity monitored by the monitoring
system continued to operate, and the
calculation of the emissions of the
pollutant or the number determined by
the method included in the permit, as
provided by paragraph (i)(13)(vii) of this
section.
(G) A signed statement by the
responsible official (as defined by the
applicable title V operating permit
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program) certifying the truth, accuracy,
and completeness of the information
provided in the report.
(ii) Deviation report. The major
stationary source owner or operator
shall promptly submit reports of any
deviations or exceedance of the Green
Group emissions limit or emissions
reduction requirement (e.g., LAER
limit), including periods where no
monitoring is available. A report
submitted pursuant to § 70.6(a)(3)(iii)(B)
of this chapter shall satisfy this
reporting requirement. The deviation
reports shall be submitted within the
time limits prescribed by the applicable
program implementing
§ 70.6(a)(3)(iii)(B) of this chapter. The
reports shall contain the following
information:
(A) The identification of owner and
operator and the permit number;
(B) The Green Group requirement that
experienced the deviation or that was
exceeded;
(C) Emissions resulting from the
deviation or the exceedance; and
(D) A signed statement by the
responsible official (as defined by the
applicable title V operating permit
program) certifying the truth, accuracy,
and completeness of the information
provided in the report.
(iii) Re-validation results. The owner
or operator shall submit to the
reviewing authority the results of any
re-validation test or method within 3
months after completion of such test or
method.
(17) Transition requirements. The
plan shall provide that the reviewing
authority may not issue a Green Group
permit that does not comply with the
requirements in paragraphs (i)(1)
through (17) of this section or their
equivalent after the Administrator has
approved regulations incorporating
these requirements into the plan. The
plan shall provide that the reviewing
authority may supersede any Green
Group permit that was established prior
to the date of approval of the plan by the
Administrator with a Green Group
permit that complies with the
requirements of paragraphs (i)(1)
through (17) of this section.
3. Section 51.166 is amended as
follows:
a. By revising paragraph (a)(7)(iv)(a);
b. By adding paragraph (a)(7)(vii);
c. By adding paragraph (b)(2)(v);
d. By revising paragraph (b)(21)(i);
e. By revising paragraph (b)(47)(iv);
f. By revising paragraph (r)(6)
introductory text; and
g. By adding paragraph (z).
The additions and revisions read as
follows:
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§ 51.166 Prevention of significant
deterioration of air quality.
(a) * * *
(7) * * *
(iv) * * *
(a) Except as otherwise provided in
paragraphs (a)(7)(v) through (vii) of this
section, and consistent with the
definition of major modification
contained in paragraph (b)(2) of this
section, a project is a major modification
for a regulated NSR pollutant if it causes
two types of emissions increases—a
significant emissions increase (as
defined in paragraph (b)(39) of this
section), and a significant net emissions
increase (as defined in paragraphs (b)(3)
and (b)(23) of this section). The project
is not a major modification if it does not
cause a significant emissions increase. If
the project causes a significant
emissions increase, then the project is a
major modification only if it also results
in a significant net emissions increase.
*
*
*
*
*
(vii) The plan shall require that for
any major stationary source with a
Green Group for a regulated NSR
pollutant, the owner or operator shall
comply with the requirements in
paragraph (z) of this section for those
emissions activities included within the
Green Group.
*
*
*
*
*
(b) * * *
(2) * * *
(v) This definition shall not apply to
approved physical changes or changes
in the method of operation within a
Green Group with respect to any Green
Group pollutant when the major
stationary source is complying with the
requirements under paragraph (z) of this
section for a Green Group for that
pollutant.
*
*
*
*
*
(21)(i) Actual emissions means the
actual rate of emissions of a regulated
NSR pollutant from an emissions unit,
as determined in accordance with
paragraphs (b)(21)(ii) through (iv) of this
section, except that this definition shall
not apply for calculating whether a
significant emissions increase has
occurred, or for establishing a PAL
under paragraph (w) of this section or a
Green Group under paragraph (z) of this
section. Instead, paragraphs (b)(40) and
(b)(47) of this section shall apply for
those purposes.
*
*
*
*
*
(47) * * *
(iv) For a PAL or Green Group for a
stationary source, the baseline actual
emissions shall be calculated for
existing electric utility steam generating
units in accordance with the procedures
contained in paragraph (b)(47)(i) of this
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section, for other existing emissions
units in accordance with the procedures
contained in paragraph (b)(47)(ii) of this
section, and for a new emissions unit in
accordance with the procedures
contained in paragraph (b)(47)(iii) of
this section.
*
*
*
*
*
(r) * * *
(6) Each plan shall provide that the
following specific provisions apply to
projects at existing emissions units at a
major stationary source (other than
projects at a Green Group or at a source
with a PAL) in circumstances where
there is a reasonable possibility that a
project that is not a part of a major
modification may result in a significant
emissions increase and the owner or
operator elects to use the method
specified in paragraphs (b)(40)(ii)(a)
through (c) of this section for calculating
projected actual emissions. Deviations
from these provisions will be approved
only if the State specifically
demonstrates that the submitted
provisions are more stringent than or at
least as stringent in all respects as the
corresponding provisions in paragraphs
(r)(6)(i) through (v) of this section.
*
*
*
*
*
(z) Green Groups. The plan shall
provide for Green Groups according to
the provisions in paragraphs (z)(1)
through (17) of this section.
(1) Applicability. The reviewing
authority may issue a permit under
regulations approved pursuant to this
section designating a Green Group at
any existing major stationary source if
the permit contains terms and
conditions assuring that the Green
Group meets the requirements in
paragraphs (z)(1) through (17) of this
section.
(i) Changes at a Green Group. Any
physical change in or change in the
method of operation authorized for a
Green Group pursuant to the
requirements in paragraphs (z)(1)
through (17) of this section that
maintains the Green Group’s total
emissions at or below the Green Group
emissions limit and maintains the Green
Group’s compliance with its best
available control technology (BACT)
limit(s):
(a) Is not a major modification for the
Green Group pollutant;
(b) Does not have to be approved
through the plan’s PSD program; and
(c) Is not subject to the provisions of
paragraph (j)(4) of this section.
(ii) Prior requirements. Except as
provided under paragraph (z)(1)(i)(c) of
this section, a major stationary source
shall continue to comply with all
remaining applicable Federal or State
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requirements, emissions limitations,
and work practice requirements that
were established prior to the effective
date of the Green Group.
(2) Definitions. The plan shall use the
definitions in paragraphs (z)(2)(i)
through (iv) of this section for the
purpose of developing and
implementing regulations that authorize
the use of Green Groups consistent with
paragraphs (z)(1) through (17) of this
section. When a term is not defined in
these paragraphs, it shall have the
meaning given in paragraph (b) or (aa)
of this section or in the Act.
(i) Green Group means a group of new
and/or existing emissions activities that
is characterized by use of a common,
dedicated air pollution control device
and that has been designated as a Green
Group by the reviewing authority in a
permit issued under regulations
approved pursuant to this section. A
Green Group is a single emissions unit
for purposes of this section.
(ii) Green Group pollutant means a
pollutant emitted from the emissions
activities that comprise the Green Group
and for which a Green Group is
designated at a major stationary source.
(iii) Green Group permit means the
major NSR permit issued by the
reviewing authority that establishes a
Green Group for a major stationary
source.
(iv) Green Group emissions limit
means an emissions limitation for the
Green Group pollutant, expressed in
tons per year, that is enforceable as a
practical matter and established for a
Green Group at a major stationary
source in accordance with paragraphs
(z)(1) through (17) of this section.
(3) Permit application requirements.
The owner or operator of a major
stationary source must request approval
for a Green Group in an application for
a major NSR permit that meets the
requirements of paragraphs (j) through
(r)(5) of this section, as applicable. As
part of a permit application requesting
a Green Group, the owner or operator of
a major stationary source shall submit
the following information to the
reviewing authority for approval:
(i) List of designated emissions
activities. A list of the emissions
activities proposed for inclusion in the
Green Group. In addition, the owner or
operator of the source shall indicate
which, if any, Federal or State
applicable requirements, emissions
limitations, or work practices apply to
each activity.
(ii) Baseline actual emissions.
Calculations of the baseline actual
emissions from included emissions
activities (with supporting
documentation). Baseline actual
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emissions are to include emissions
associated not only with operation of
the activity, but also emissions
associated with startup, shutdown, and
malfunction.
(iii) Monitoring data conversion
procedures. The calculation procedures
that the major stationary source owner
or operator proposes to use to convert
the monitoring system data to monthly
emissions and annual emissions based
on a 12-month rolling total for each
month as required by paragraph
(z)(15)(i) of this section.
(iv) Description. A description of the
equipment that comprises the Green
Group, including a description of
existing emissions activities, proposed
physical changes or changes in method
of operation (which may include the
addition of new emissions activities),
and the common air pollution control
device. The description must provide
information about maximum total
emissions that will be generated by the
Green Group’s emissions activities and
the associated characteristics of the
combined emissions streams (including
the worst-case emissions stream) that
will be ducted to the common air
pollution control device. The
description must be sufficient:
(a) To allow the reviewing authority
to distinguish changes proposed to be
authorized in the Green Group from
unauthorized changes; and
(b) To enable the reviewing authority
to determine BACT for the Green Group
consistent with paragraphs (z)(4)(ii) and
(z)(7)(vi) of this section.
(v) Control technology demonstration.
A demonstration that the proposed
control technology represents BACT.
Such a demonstration shall confirm that
the emissions reduction capacity of the
proposed common control device is
sufficient to meet the relevant emissions
reduction requirement, considering the
maximum total emissions from the
Green Group and the associated
characteristics of the combined
emissions streams that will be ducted to
the common air pollution control
device. The BACT demonstration shall
be based on worst-case emissions from
the new and existing emissions
activities authorized for the Green
Group.
(vi) Monitoring system. A proposed
monitoring system sufficient to meet the
requirements of paragraph (z)(13) of this
section with respect to Green Group
emissions limit(s) and the requirements
of paragraph (z)(14) of this section with
respect to BACT-related limitations.
(vii) Proposed Green Group emissions
limit. The proposed Green Group
emissions limit, in tons per year, with
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supporting documentation including,
but not limited to, the following:
(a) Baseline actual emissions of
existing emissions activities proposed to
be included in the Green Group,
adjusted to reflect the application of
BACT; and
(b) The amount of emissions growth
proposed for the Green Group as the
result of the proposed physical,
operational, and other changes.
(4) General requirements for
designating a Green Group. The plan
shall provide that the reviewing
authority may designate a Green Group
at an existing major stationary source
through issuance of a PSD permit under
regulations approved pursuant to this
section, provided that in addition, at a
minimum, the requirements in
paragraphs (z)(4)(i) through (vii) of this
section are met.
(i) Green Group emissions limit. The
reviewing authority, consistent with
regulations approved pursuant to
paragraph (z)(6) of this section, shall
establish a Green Group emissions limit
in tons per year for those emissions
activities included under the Green
Group (including any new emissions
activities added within the Green
Group). For each month during the
Green Group effective period after the
first 12 months of establishing the Green
Group, the major stationary source
owner or operator shall show that the
sum of the monthly emissions from each
included emissions activity for the
previous 12 consecutive months is less
than or equal to the Green Group
emissions limit (i.e. a 12-month total,
rolled monthly). For each month during
the first 11 months from the Green
Group effective date, the major
stationary source owner or operator
shall show that the sum of the preceding
monthly emissions from the Green
Group effective date for each emissions
activity under the Green Group is less
than or equal to the Green Group
emissions limit.
(ii) BACT emissions limit. The
reviewing authority shall determine
BACT for the emissions of the Green
Group pollutant from the group of
emissions activities designated as a
Green Group. The BACT emissions limit
shall ensure that the emissions of the
emissions activities included in the
Green Group are ducted to a common,
dedicated air pollution control device
and ensure compliance with any
applicable emissions limitation under
the State Implementation Plan and each
applicable emission standard and
standard of performance under 40 CFR
parts 60 and 61. The control device, in
combination with any additional control
measures consistent with paragraphs
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(z)(4)(ii)(a) and (b) of this section, must
achieve the BACT level of emissions
reductions for the Green Group
pollutant.
(a) In addition to the requirement to
duct emissions from the Green Group to
a common air pollution control device,
additional control measures such as
pollution prevention (as defined under
paragraph (b)(38) of this section), work
practices, and/or operational standards
may be defined as part of the approved
control measures.
(b) Pollution prevention measures that
have been determined to represent
BACT may be approved to apply during
certain periods of operation. The
included emissions activities must have
ductwork extending to the common air
pollution control device, but the owner
or operator would be allowed to bypass
the control device during periods when
the pollution prevention alternative is
in use, consistent with the BACT
determination. Emissions activities that
exclusively use the pollution prevention
alternative and never use the common
air pollution control device may not be
included in the Green Group.
(iii) Permit content. The Green Group
permit shall contain all the
requirements of paragraph (z)(7) of this
section.
(iv) Included emissions. The Green
Group emissions limit shall include
fugitive emissions of the Green Group
pollutant, to the extent quantifiable,
from all emissions activities included
under the Green Group.
(v) Regulated pollutant. Each Green
Group shall regulate emissions of only
one pollutant. However, the same
collection of emissions activities may be
designated separately as a Green Group
for another pollutant.
(vi) Effective period. Each Green
Group designation shall have an
effective period of 10 years.
(vii) Monitoring, recordkeeping, and
reporting. The Green Group permit shall
require the owner or operator to comply
with the monitoring, recordkeeping, and
reporting requirements in paragraphs
(z)(13) through (16) of this section for
each included emissions activity.
(5) General provisions for Green
Groups. The plan shall require that the
provisions set out in paragraphs (z)(5)(i)
through (iv) apply to Green Groups:
(i) Any project for which the owner or
operator begins actual construction after
the effective date of a Green Group
designation and before its expiration
date will be considered to have occurred
while the emissions unit was a Green
Group.
(ii) At no time (during or after the
Green Group effective period) are
emissions reductions of a Green Group
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pollutant that occur during the Green
Group effective period creditable as
decreases for purposes of offsets under
§ 51.165(a)(3)(ii) unless the Green Group
emissions limit is reduced by the
amount of such emissions reductions
and such reductions would be
creditable in the absence of the Green
Group designation. No emissions
reduction credit can be generated for
emissions growth that was authorized
under the Green Group permit, but
never realized.
(iii) At no time (during or after the
Green Group effective period) are
emissions increases or reductions of a
Green Group pollutant that occur during
the Green Group effective period
creditable for purposes of calculating a
net emissions increase under paragraph
(b)(3) of this section (that is, must not
be used in a ‘‘netting analysis’’), unless
the Green Group emissions limit is
reduced by the amount of such
emissions reductions and such
reductions would be creditable in the
absence of the Green Group designation.
No emissions reduction credit can be
generated for emissions growth that was
authorized under the Green Group
permit, but never realized.
(iv) The Green Group designation of
an emissions unit is not affected by
redesignation of the attainment status of
the area in which it is located. That is,
if a Green Group is located in an
attainment area and the area is
redesignated to nonattainment, its Green
Group designation is not affected.
Similarly, redesignation from
nonattainment to attainment does not
affect the Green Group designation.
However, if an existing Green Group
designation expires, it must re-qualify
under the requirements that are
currently applicable in the area.
(6) Setting the 10-year Green Group
emissions limit. The plan shall provide
that the Green Group emissions limit is
to be established as follows:
(i) Except as provided in paragraphs
(z)(6)(ii) through (iv) of this section, the
Green Group emissions limit shall be
established as the sum of the baseline
actual emissions (as defined in
paragraph (b)(47) of this section) of the
Green Group pollutant for each
emissions activity included in the Green
Group. When establishing the Green
Group emissions limit, for a Green
Group pollutant, a single period of 24
consecutive months must be used to
determine the baseline actual emissions
for all existing emissions activities.
However, a different period of 24
consecutive months may be used for
each different Green Group pollutant.
Emissions associated with activities that
were permanently shut down after this
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24-month period must be subtracted
from the Green Group emissions limit.
The reviewing authority shall specify a
reduced Green Group emissions limit(s)
(in tons/yr) in the Green Group permit
to become effective on the future
compliance date(s) of any applicable
Federal or State regulatory
requirement(s) that the reviewing
authority is aware of prior to issuance
of the Green Group permit.
(ii) For activities (which do not
include modifications to existing units)
on which actual construction began
after the 24-month period, in lieu of
adding the baseline actual emissions as
specified in paragraph (z)(6)(i) of this
section, the emissions must be added to
the Green Group emissions limit in an
amount equal to the potential to emit of
the activities.
(iii) The reviewing authority shall
establish the Green Group emissions
level by adjusting the total derived
according to paragraphs (z)(6)(i) and (ii)
of this section to reflect:
(a) The application of BACT; and
(b) An additional amount of actual
emissions consistent with the growth
approved for the Green Group.
(iv) Notwithstanding the methodology
set out above in paragraphs (z)(6)(i)
through (iii) of this section, the
reviewing authority shall reduce the
Green Group emissions limit and/or
establish short-term emissions limits as
necessary to meet other applicable
requirements of this section, including
the requirements of paragraphs (k) and
(p).
(7) Content of the Green Group
permit. The plan shall require that the
Green Group permit contain the
elements listed in paragraphs (z)(7)(i)
through (xiv) of this section and any
other provisions that the reviewing
authority deems necessary to implement
the Green Group.
(i) The Green Group pollutant.
(ii) A description of the equipment
that comprises the Green Group,
including a description of existing
emissions activities, any authorized
physical changes or changes in method
of operation, and the common air
pollution control device. The
description must provide information
about the maximum total emissions that
will be generated by the Green Group’s
emissions activities and the associated
characteristics of the combined
emissions streams that will be ducted to
the common air pollution control
device. The description must be
sufficient to distinguish, when a change
is subsequently made in the Green
Group, whether that change was
authorized under the Green Group
permit.
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(iii) A statement designating the
described equipment as a Green Group.
(iv) The Green Group emissions limit
(in terms of a 12-month total, rolled
monthly) for the group of emissions
activities included under the Green
Group.
(v) Any shorter-term emissions limits
that are necessary to safeguard ambient
air quality, as determined according to
the requirements of the regulations
approved pursuant to this section.
(vi) All emissions limitations and
work practice requirements established
to ensure that BACT is met.
(vii) The Green Group effective date
and the expiration date of the Green
Group (i.e., the Green Group effective
period). If the source owner or operator
must construct a new air pollution
control device or modify an existing
device as a result of the BACT
determination for the Green Group, the
permit may provide that the existing
emissions activities within the Green
Group are not required to meet the
BACT emissions limitation(s) or the
Green Group emissions limit until the
new or modified air pollution control
device is in operation. (That is, such
emissions activities may continue to
meet pre-existing emissions limitations
until that time.) However, new and
modified emissions activities within the
Green Group must be subject to BACT
upon startup. In addition, the Green
Group must be subject to the Green
Group emissions limit (and associated
monitoring, recordkeeping, and
reporting requirements) beginning at the
time that the new or modified air
pollution control device is placed in
operation.
(viii) Specification in the Green Group
permit that if a major stationary source
owner or operator applies to renew a
Green Group in accordance with
paragraph (z)(11) of this section before
the end of the effective period, then the
Green Group shall not expire at the end
of the effective period. It shall remain in
effect until a new Green Group permit
is issued by the reviewing authority.
(ix) A requirement that emissions
calculations for compliance purposes
must include emissions from startups,
shutdowns, and malfunctions.
(x) A requirement that, once the Green
Group expires, the major stationary
source is subject to the requirements of
paragraph (z)(10) of this section.
(xi) The calculation procedures that
the major stationary source owner or
operator shall use to convert the
monitoring system data to monthly
emissions and annual emissions based
on a 12-month rolling total as required
by paragraph (z)(15)(i) of this section.
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(xii) A requirement that the major
stationary source owner or operator
meet all applicable requirements for
monitoring, testing, and operation in
accordance with the provisions of
paragraphs (z)(13) and (14) of this
section.
(xiii) A requirement to retain the
records required under paragraph (z)(15)
of this section on site. Such records may
be retained in an electronic format.
(xiv) A requirement to submit the
reports required under paragraph (z)(16)
of this section by the required
deadlines.
(8) Green Group effective period. The
plan shall require that the reviewing
authority specify an effective period of
10 years. The effective period begins
upon the Green Group effective date,
which is the date that the Green Group
permit becomes effective.
(9) Reopening of the Green Group
permit. The plan shall provide that the
requirements in paragraphs (z)(9)(i)
through (iii) of this section apply to
reopening Green Group permits.
(i) Mandatory reopenings. During the
Green Group effective period, the
reviewing authority must reopen the
Green Group permit to:
(a) Correct typographical/calculation
errors made in setting the Green Group
emissions limit or reflect a more
accurate determination of emissions
used to establish this limit;
(b) Reduce the Green Group emissions
limit if the owner or operator of the
major stationary source creates
creditable emissions reductions for use
as offsets under § 51.165(a)(3)(ii); and
(c) Reduce the Green Group emissions
limit if the owner or operator of the
major stationary source creates
creditable emissions reductions for use
in a netting analysis under paragraph
(b)(3) of this section.
(ii) Discretionary reopenings. The
reviewing authority shall have
discretion to reopen the Green Group
permit for the purposes listed in
paragraphs (z)(9)(ii)(a) through (c) of
this section. If the reviewing authority
declines to reopen the Green Group
permit for any of these purposes, the
Green Group emissions limit must be
adjusted upon expiration of the Green
Group designation or upon renewal of
the source’s title V permit, whichever
comes first. The major stationary source
owner or operator is responsible for
compliance with any new applicable
requirements, regardless of when the
permit is reopened and adjusted.
(a) To reduce the Green Group
emissions limit to reflect newly
applicable Federal requirements (for
example, NSPS) with compliance dates
after the Green Group effective date;
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(b) To reduce the emissions limit
consistent with any other requirement,
that is enforceable as a practical matter,
and that the State may impose on the
major stationary source under the State
Implementation Plan; and
(c) To reduce the emissions limit if
the reviewing authority determines that
a reduction is necessary to avoid
causing or contributing to a NAAQS or
PSD increment violation, or to an
adverse impact on an air quality related
value that has been identified for a
Federal Class I area by a Federal Land
Manager and for which information is
available to the general public.
(iii) Required process. Except for the
permit reopening in paragraph
(z)(9)(i)(a) of this section for the
correction of typographical/calculation
errors that do not increase the Green
Group emissions limit, all other
reopenings shall be carried out in
accordance with the public
participation requirements of paragraph
(q) of this section.
(10) Expiration of a Green Group. The
plan shall require that any Green Group
designation that is not renewed in
accordance with the procedures in
paragraph (z)(11) of this section shall
expire at the end of its effective period.
After expiration of the Green Group
designation, the following provisions
apply:
(i) The emissions unit defined by the
Green Group remains an emissions unit
for purposes of major NSR and remains
subject to the BACT control
requirements; Green Group emissions
limit; any shorter-term emissions limits;
and monitoring, recordkeeping,
reporting, and testing requirements
imposed by the Green Group permit.
(ii) The major stationary source owner
or operator shall continue to comply
with any State or Federal applicable
requirements (BACT, RACT, NSPS, etc.)
that may have applied either during or
prior to the Green Group effective
period.
(iii) Any subsequent physical change
or change in the method of operation at
the emissions unit defined by the Green
Group will be subject to PSD
requirements if such change meets the
definition of major modification in
paragraph (b)(2) of this section.
(11) Renewal of a Green Group. The
plan shall require that the following
provisions apply to renewal of a Green
Group:
(i) Required procedures. A Green
Group may be renewed through
issuance of a new major NSR permit
according to all the requirements of this
paragraph (z) for the initial Green Group
designation.
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(ii) Application deadline. A major
stationary source owner or operator
shall submit a timely application to the
reviewing authority to request renewal
of a Green Group. A timely application
is one that is submitted at least 6
months prior to, but not earlier than 18
months from, the date that the Green
Group designation would otherwise
expire. This deadline for application
submittal is to ensure that the Green
Group designation will not expire before
the Green Group is renewed. If the
owner or operator of a major stationary
source submits a complete application
to renew the Green Group within this
time period, then the Green Group shall
continue to be effective until the new
PSD permit with the renewed Green
Group is issued.
(12) Increasing a Green Group
emissions limit during its effective
period. The plan shall provide that the
reviewing authority may increase a
Green Group emissions limit during its
effective period only if the increase is
contained in a new permit incorporating
the increase into a new Green Group
consistent with the requirements of the
regulations approved pursuant to this
section.
(13) Monitoring requirements for
Green Group emissions limitations. The
plan shall provide that the following
monitoring requirements apply to Green
Groups.
(i) General requirements.
(a) Each Green Group permit must
contain enforceable requirements for the
monitoring system that accurately
determines, in terms of mass per unit of
time, emissions of the Green Group
pollutant from the emissions activities
under the Green Group. Any monitoring
system authorized for use in the Green
Group permit must be based on sound
science and meet generally acceptable
scientific procedures for data quality
and manipulation. Additionally, the
information generated by such system
must meet minimum legal requirements
for admissibility in a judicial
proceeding to enforce the Green Group
permit.
(b) The Green Group monitoring
system must employ one or more of the
four general monitoring approaches
meeting the minimum requirements set
forth in paragraphs (z)(13)(ii)(a) through
(d) of this section and must be approved
by the reviewing authority.
(c) Notwithstanding paragraph
(z)(13)(i)(b) of this section, you may also
employ an alternative monitoring
approach that meets paragraph
(z)(13)(i)(a) of this section if approved
by the reviewing authority.
(b) Failure to use a monitoring system
that meets the requirements of this
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section renders the Green Group
invalid.
(ii) Minimum performance
requirements for approved monitoring
approaches. The following are
acceptable general monitoring
approaches when conducted in
accordance with the minimum
requirements in paragraphs (z)(13)(iii)
through (ix) of this section:
(a) Mass balance calculations for
activities using coatings or solvents;
(b) CEMS;
(c) CPMS or PEMS; and
(d) Emissions factors.
(iii) Mass balance calculations. An
owner or operator using mass balance
calculations to monitor the Green Group
pollutant emissions from activities
using coating or solvents shall meet the
following requirements:
(a) Provide a demonstrated means of
validating the published content of the
Green Group pollutant that is contained
in or created by all materials used in or
at the emissions activity;
(b) Assume that the emissions activity
emits all of the Green Group pollutant
that is contained in or created by any
raw material or fuel used in or at the
emissions activity, if it cannot otherwise
be accounted for in the process; and
(c) Where the vendor of a material or
fuel, which is used in or at the
emissions activity, publishes a range of
pollutant content from such material,
the owner or operator must use the
highest value of the range to calculate
the Green Group pollutant emissions
unless the reviewing authority
determines there is site-specific data or
a site-specific monitoring program to
support another content within the
range.
(iv) CEMS. An owner or operator
using CEMS to monitor Green Group
pollutant emissions shall meet the
following requirements:
(a) CEMS must comply with
applicable Performance Specifications
found in 40 CFR part 60, appendix B;
and
(b) CEMS must sample, analyze, and
record data at least every 15 minutes
while the emissions activity is
operating.
(v) CPMS or PEMS. An owner or
operator using CPMS or PEMS to
monitor Green Group pollutant
emissions shall meet the following
requirements:
(a) The CPMS or the PEMS must be
based on current site-specific data
demonstrating a correlation between the
monitored parameter(s) and the Green
Group pollutant emissions across the
range of operation of the emissions
activity; and
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(b) Each CPMS or PEMS must sample,
analyze, and record data at least every
15 minutes, or at another less frequent
interval approved by the reviewing
authority, while the emissions activity
is operating.
(vi) Emissions factors. An owner or
operator using emissions factors to
monitor Green Group pollutant
emissions shall meet the following
requirements:
(a) All emissions factors shall be
adjusted, if appropriate, to account for
the degree of uncertainty or limitations
in the factors’ development;
(b) The emissions activity shall
operate within the designated range of
use for the emissions factor, if
applicable; and
(c) If technically practicable, the
owner or operator of a significant or
major emissions activity that relies on
an emissions factor to calculate Green
Group pollutant emissions shall
conduct validation through performance
testing or other scientifically valid
means approved by the reviewing
authority to determine a site-specific
emissions factor. Such testing or other
means shall occur within 6 months of
Green Group permit issuance, unless the
reviewing authority determines that
testing is not required.
(vii) Missing data procedures. A
source owner or operator must record
and report maximum potential
emissions without considering
enforceable emissions limitations or
operational restrictions for an emissions
activity during any period of time that
there is no monitoring data, unless
another method for determining
emissions during such periods is
specified in the Green Group permit.
(viii) Alternative requirements.
Notwithstanding the requirements in
paragraphs (z)(13)(iii) through (vii) of
this section, where an owner or operator
of an emissions activity cannot
demonstrate a correlation between the
monitored parameter(s) and the Green
Group pollutant emissions rate at all
operating points of the emissions
activity, the reviewing authority shall, at
the time of permit issuance:
(a) Establish default value(s) for
determining compliance with the Green
Group emissions limit based on the
highest potential emissions reasonably
estimated at such operating point(s); or
(b) Determine that operation of the
emissions activity during operating
conditions when there is no correlation
between monitored parameter(s) and the
Green Group pollutant emissions is a
violation of the Green Group emissions
limit.
(ix) Re-validation. All data used to
establish the Green Group pollutant
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emissions must be re-validated through
performance testing or other
scientifically valid means approved by
the reviewing authority. Such testing
must occur at least once every 5 years
after issuance of the Green Group.
(14) Additional monitoring
requirements for BACT. The plan shall
provide that the permit must also
require the owner or operator with a
Green Group to monitor, measure, and
record data sufficient to determine
whether:
(i) The emissions reduction measures
(including the Green Group air
pollution control device) meet the
emissions limitations and/or work
practice requirements adopted in
conjunction with BACT; and
(ii) The demonstrated capacity of the
Green Group air pollution control
device was exceeded by the emissions
stream(s) directed to it at any time
during the reporting period. The
capacity of the control device is
considered exceeded if the
characteristics of the emissions stream
entering the device are outside the range
for which it has been demonstrated that
the device can achieve BACT, absent
valid monitoring data (from a
continuous monitoring system or other
monitoring approach approved for such
use by the reviewing authority) showing
compliance with BACT at the new
operating level. A period of exceedance
is considered a deviation for purposes of
recordkeeping and reporting.
(15) Recordkeeping requirements. The
plan shall require that the following
recordkeeping requirements apply to
Green Groups:
(i) Records to determine compliance.
The Green Group permit shall require
an owner or operator to retain a copy of
all records necessary to determine
compliance with any requirement of
paragraph (z) of this section and of the
Green Group permit, including a
determination of each emissions
activity’s 12-month rolling total
emissions, for 5 years from the date of
such record.
(ii) Other records. The Green Group
permit shall require an owner or
operator to retain a copy of the
following records for the duration of the
Green Group effective period plus 5
years:
(a) A copy of the Green Group permit
application and any applications for
revisions to the Green Group permit;
and
(b) Each annual certification of
compliance pursuant to title V and the
data relied on in certifying the
compliance.
(16) Reporting and notification
requirements. The plan shall require the
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owner or operator to submit semiannual monitoring reports and prompt
deviation reports to the reviewing
authority in accordance with the
applicable title V operating permit
program. The reports shall meet the
requirements in paragraphs (z)(16)(i)
through (iii) of this section.
(i) Semi-annual report. The semiannual report shall be submitted to the
reviewing authority within 30 days of
the end of each reporting period. This
report shall contain the information
required in paragraphs (z)(16)(i)(a)
through (g) of this section.
(a) The identification of owner and
operator and the permit number.
(b) Total annual emissions (tons per
year) from the emissions activities
included under the Green Group, based
on a 12-month rolling total for each
month in the reporting period recorded
pursuant to paragraph (z)(15)(i) of this
section.
(c) All data relied upon, including,
but not limited to, any Quality
Assurance or Quality Control data, in
calculating the monthly and annual
Green Group pollutant emissions.
(d) A list of any emissions activities
included under the Green Group that
were added during the preceding 6month period.
(e) The number, duration, and cause
of any deviations or monitoring
malfunctions (other than the time
associated with zero and span
calibration checks), and any corrective
action taken.
(f) A notification of a shutdown of any
monitoring system, whether the
shutdown was permanent or temporary,
the reason for the shutdown, the
anticipated date that the monitoring
system will be fully operational or
replaced with another monitoring
system, and whether the emissions
activity monitored by the monitoring
system continued to operate, and the
calculation of the emissions of the
pollutant or the number determined by
the method included in the permit, as
provided by paragraph (z)(13)(vii) of
this section.
(g) A signed statement by the
responsible official (as defined by the
applicable title V operating permit
program) certifying the truth, accuracy,
and completeness of the information
provided in the report.
(ii) Deviation report. The major
stationary source owner or operator
shall promptly submit reports of any
deviations or exceedance of the Green
Group emissions limit or emissions
reduction requirement (e.g., BACT
limit), including periods where no
monitoring is available. A report
submitted pursuant to § 70.6(a)(3)(iii)(B)
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of this chapter shall satisfy this
reporting requirement. The deviation
reports shall be submitted within the
time limits prescribed by the applicable
program implementing
§ 70.6(a)(3)(iii)(B) of this chapter. The
reports shall contain the following
information:
(a) The identification of owner and
operator and the permit number;
(b) The Green Group requirement that
experienced the deviation or that was
exceeded;
(c) Emissions resulting from the
deviation or the exceedance; and
(d) A signed statement by the
responsible official (as defined by the
applicable title V operating permit
program) certifying the truth, accuracy,
and completeness of the information
provided in the report.
(iii) Re-validation results. The owner
or operator shall submit to the
reviewing authority the results of any
re-validation test or method within 3
months after completion of such test or
method.
(17) Transition requirements. The
plan shall provide that the reviewing
authority may not issue a Green Group
permit that does not comply with the
requirements in paragraphs (z)(1)
through (17) of this section or their
equivalent after the Administrator has
approved regulations incorporating
these requirements into the plan. The
plan shall provide that the reviewing
authority may supersede any Green
Group permit that was established prior
to the date of approval of the plan by the
Administrator with a Green Group
permit that complies with the
requirements of paragraphs (z)(1)
through (17) of this section.
PART 52—[AMENDED]
4. The authority citation for part 52
continues to read as follows:
Authority: 42 U.S.C. 7401 et seq.
Subpart A—[Amended]
5. Section 52.21 is amended as
follows:
a. By revising paragraph (a)(2)(iv)(a);
b. By adding paragraph (a)(2)(vii);
c. By adding paragraph (b)(2)(v);
d. By revising paragraph (b)(21)(i);
e. By revising paragraph (b)(48)(iv);
f. By revising paragraph (r)(6)
introductory text; and
g. By adding paragraph (dd).
The additions and revisions read as
follows:
§ 52.21 Prevention of significant
deterioration of air quality.
(a) * * *
(2) * * *
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(iv) * * *
(a) Except as otherwise provided in
paragraphs (a)(2)(v) through (vii) of this
section, and consistent with the
definition of major modification
contained in paragraph (b)(2) of this
section, a project is a major modification
for a regulated NSR pollutant if it causes
two types of emissions increases—a
significant emissions increase (as
defined in paragraph (b)(40) of this
section), and a significant net emissions
increase (as defined in paragraphs (b)(3)
and (b)(23) of this section). The project
is not a major modification if it does not
cause a significant emissions increase. If
the project causes a significant
emissions increase, then the project is a
major modification only if it also results
in a significant net emissions increase.
*
*
*
*
*
(vii) For any major stationary source
with a Green Group for a regulated NSR
pollutant, the owner or operator shall
comply with the requirements in
paragraph (dd) of this section for those
emissions activities included within the
Green Group.
*
*
*
*
*
(b) * * *
(2) * * *
(v) This definition shall not apply to
approved physical changes or changes
in the method of operation within a
Green Group with respect to any Green
Group pollutant when the major
stationary source is complying with the
requirements under paragraph (dd) of
this section for a Green Group for that
pollutant.
*
*
*
*
*
(21)(i) Actual emissions means the
actual rate of emissions of a regulated
NSR pollutant from an emissions unit,
as determined in accordance with
paragraphs (b)(21)(ii) through (iv) of this
section, except that this definition shall
not apply for calculating whether a
significant emissions increase has
occurred, or for establishing a PAL
under paragraph (aa) of this section or
a Green Group under paragraph (dd) of
this section. Instead, paragraphs (b)(41)
and (b)(48) of this section shall apply for
those purposes.
*
*
*
*
*
(48) * * *
(iv) For a PAL or Green Group for a
stationary source, the baseline actual
emissions shall be calculated for
existing electric utility steam generating
units in accordance with the procedures
contained in paragraph (b)(48)(i) of this
section, for other existing emissions
units in accordance with the procedures
contained in paragraph (b)(48)(ii) of this
section, and for a new emissions unit in
accordance with the procedures
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contained in paragraph (b)(48)(iii) of
this section.
*
*
*
*
*
(r) * * *
(6) The provisions of this paragraph
(r)(6) apply to projects at an existing
emissions unit at a major stationary
source (other than projects at a Green
Group or at a source with a PAL) in
circumstances where there is a
reasonable possibility that a project that
is not a part of a major modification may
result in a significant emissions increase
and the owner or operator elects to use
the method specified in paragraphs
(b)(41)(ii)(a) through (c) of this section
for calculating projected actual
emissions.
*
*
*
*
*
(dd) Green Groups. The provisions in
paragraphs (dd)(1) through (17) of this
section govern Green Groups.
(1) Applicability. The Administrator
may issue a permit pursuant to this
section designating a Green Group at
any existing major stationary source if
the permit contains terms and
conditions assuring that the Green
Group meets the requirements in
paragraphs (dd)(1) through (17) of this
section.
(i) Changes at a Green Group. Any
physical change in or change in the
method of operation authorized for a
Green Group pursuant to the
requirements in paragraphs (dd)(1)
through (17) of this section that
maintains the Green Group’s total
emissions at or below the Green Group
emissions limit and maintains the Green
Group’s compliance with its best
available control technology (BACT)
limit(s):
(a) Is not a major modification for the
Green Group pollutant;
(b) Does not have to be approved
through the PSD program; and
(c) Is not subject to the provisions of
paragraphs (j)(4) and (r)(2) of this
section.
(ii) Prior requirements. Except as
provided under paragraph (dd)(1)(i)(c)
of this section, a major stationary source
shall continue to comply with all
remaining applicable Federal or State
requirements, emissions limitations,
and work practice requirements that
were established prior to the effective
date of the Green Group.
(2) Definitions. For the purposes of
this paragraph (dd), the definitions in
paragraphs (dd)(2)(i) through (iv) of this
section apply. When a term is not
defined in these paragraphs, it shall
have the meaning given in paragraph (b)
or (aa) of this section or in the Act.
(i) Green Group means a group of new
and/or existing emissions activities that
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is characterized by use of a common,
dedicated air pollution control device
and that has been designated as a Green
Group by the Administrator in a permit
issued pursuant to this section. A Green
Group is a single emissions unit for
purposes of this section.
(ii) Green Group pollutant means a
pollutant emitted from the emissions
activities that comprise the Green Group
and for which a Green Group is
designated at a major stationary source.
(iii) Green Group permit means the
major NSR permit issued by the
Administrator that establishes a Green
Group for a major stationary source.
(iv) Green Group emissions limit
means an emissions limitation for the
Green Group pollutant, expressed in
tons per year, that is enforceable as a
practical matter and established for a
Green Group at a major stationary
source in accordance with paragraphs
(dd)(1) through (17) of this section.
(3) Permit application requirements.
The owner or operator of a major
stationary source must request approval
for a Green Group in an application for
a major NSR permit that meets the
requirements of paragraphs (j) through
(r)(5) of this section, as applicable. As
part of a permit application requesting
a Green Group, the owner or operator of
a major stationary source shall submit
the following information to the
Administrator for approval:
(i) List of designated emissions
activities. A list of the emissions
activities proposed for inclusion in the
Green Group. In addition, the owner or
operator of the source shall indicate
which, if any, Federal or State
applicable requirements, emissions
limitations, or work practices apply to
each activity.
(ii) Baseline actual emissions.
Calculations of the baseline actual
emissions from included emissions
activities (with supporting
documentation). Baseline actual
emissions are to include emissions
associated not only with operation of
the activity, but also emissions
associated with startup, shutdown, and
malfunction.
(iii) Monitoring data conversion
procedures. The calculation procedures
that the major stationary source owner
or operator proposes to use to convert
the monitoring system data to monthly
emissions and annual emissions based
on a 12-month rolling total for each
month as required by paragraph
(dd)(15)(i) of this section.
(iv) Description. A description of the
equipment that comprises the Green
Group, including a description of
existing emissions activities, proposed
physical changes or changes in method
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of operation (which may include the
addition of new emissions activities),
and the common air pollution control
device. The description must provide
information about maximum total
emissions that will be generated by the
Green Group’s emissions activities and
the associated characteristics of the
combined emissions streams (including
the worst-case emissions stream) that
will be ducted to the common air
pollution control device. The
description must be sufficient:
(a) To allow the Administrator to
distinguish changes proposed to be
authorized in the Green Group from
unauthorized changes; and
(b) To enable the Administrator to
determine BACT for the Green Group
consistent with paragraphs (dd)(4)(ii)
and (dd)(7)(vi) of this section.
(v) Control technology demonstration.
A demonstration that the proposed
control technology represents BACT.
Such a demonstration shall confirm that
the emissions reduction capacity of the
proposed common control device is
sufficient to meet the relevant emissions
reduction requirement, considering the
maximum total emissions from the
Green Group and the associated
characteristics of the combined
emissions streams that will be ducted to
the common air pollution control
device. The BACT demonstration shall
be based on worst-case emissions from
the new and existing emissions
activities authorized for the Green
Group.
(vi) Monitoring system. A proposed
monitoring system sufficient to meet the
requirements of paragraph (dd)(13) of
this section with respect to Green Group
emissions limit(s) and the requirements
of paragraph (dd)(14) of this section
with respect to BACT-related
limitations.
(vii) Proposed Green Group emissions
limit. The proposed Green Group
emissions limit, in tons per year, with
supporting documentation including,
but not limited to, the following:
(a) Baseline actual emissions of
existing emissions activities proposed to
be included in the Green Group,
adjusted to reflect the application of
BACT; and
(b) The amount of emissions growth
proposed for the Green Group as the
result of the proposed physical,
operational, and other changes.
(4) General requirements for
designating a Green Group. The
Administrator may designate a Green
Group at an existing major stationary
source through issuance of a PSD permit
according to the requirements of this
section, provided that in addition the
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requirements in paragraphs (dd)(4)(i)
through (vii) of this section are met.
(i) Green Group emissions limit. The
Administrator, consistent with
paragraph (dd)(6) of this section, shall
establish a Green Group emissions limit
in tons per year for those emissions
activities included under the Green
Group (including any new emissions
activities added within the Green
Group). For each month during the
Green Group effective period after the
first 12 months of establishing the Green
Group, the major stationary source
owner or operator shall show that the
sum of the monthly emissions from each
included emissions activity for the
previous 12 consecutive months is less
than or equal to the Green Group
emissions limit (i.e. a 12-month total,
rolled monthly). For each month during
the first 11 months from the Green
Group effective date, the major
stationary source owner or operator
shall show that the sum of the preceding
monthly emissions from the Green
Group effective date for each emissions
activity under the Green Group is less
than or equal to the Green Group
emissions limit.
(ii) BACT emissions limit. The
Administrator shall determine BACT for
the emissions of the Green Group
pollutant from the group of emissions
activities designated as a Green Group.
The BACT emissions limit shall ensure
that the emissions of the emissions
activities included in the Green Group
are ducted to a common, dedicated air
pollution control device and ensure
compliance with any applicable
emissions limitation under the State
Implementation Plan and each
applicable emission standard and
standard of performance under 40 CFR
parts 60 and 61. The control device, in
combination with any additional control
measures consistent with paragraphs
(dd)(4)(ii)(a) and (b) of this section,
must achieve the BACT level of
emissions reductions for the Green
Group pollutant.
(a) In addition to the requirement to
duct emissions from the Green Group to
a common air pollution control device,
additional control measures such as
pollution prevention (as defined under
paragraph (b)(39) of this section), work
practices, and/or operational standards
may be defined as part of the approved
control measures.
(b) Pollution prevention measures that
have been determined to represent
BACT may be approved to apply during
certain periods of operation. The
included emissions activities must have
ductwork extending to the common air
pollution control device, but the owner
or operator would be allowed to bypass
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the control device during periods when
the pollution prevention alternative is
in use, consistent with the BACT
determination. Emissions activities that
exclusively use the pollution prevention
alternative and never use the common
air pollution control device may not be
included in the Green Group.
(iii) Permit content. The Green Group
permit shall contain all the
requirements of paragraph (dd)(7) of this
section.
(iv) Included emissions. The Green
Group emissions limit shall include
fugitive emissions of the Green Group
pollutant, to the extent quantifiable,
from all emissions activities included
under the Green Group.
(v) Regulated pollutant. Each Green
Group shall regulate emissions of only
one pollutant. However, the same
collection of emissions activities may be
designated separately as a Green Group
for another pollutant.
(vi) Effective period. Each Green
Group designation shall have an
effective period of 10 years.
(vii) Monitoring, recordkeeping, and
reporting. The Green Group permit shall
require the owner or operator to comply
with the monitoring, recordkeeping, and
reporting requirements provided in
paragraphs (dd)(13) through (16) of this
section for each included emissions
activity.
(5) General provisions for Green
Groups. The provisions set out in
paragraphs (dd)(5)(i) through (iv) apply
to Green Groups:
(i) Any project for which the owner or
operator begins actual construction after
the effective date of a Green Group
designation and before its expiration
date will be considered to have occurred
while the emissions unit was a Green
Group.
(ii) At no time (during or after the
Green Group effective period) are
emissions reductions of a Green Group
pollutant that occur during the Green
Group effective period creditable as
decreases for purposes of offsets under
§ 51.165(a)(3)(ii) of this chapter unless
the Green Group emissions limit is
reduced by the amount of such
emissions reductions and such
reductions would be creditable in the
absence of the Green Group designation.
No emissions reduction credit can be
generated for emissions growth that was
authorized under the Green Group
permit, but never realized.
(iii) At no time (during or after the
Green Group effective period) are
emissions increases or reductions of a
Green Group pollutant that occur during
the Green Group effective period
creditable for purposes of calculating a
net emissions increase under paragraph
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(b)(3) of this section (that is, must not
be used in a ‘‘netting analysis’’), unless
the Green Group emissions limit is
reduced by the amount of such
emissions reductions and such
reductions would be creditable in the
absence of the Green Group designation.
No emissions reduction credit can be
generated for emissions growth that was
authorized under the Green Group
permit, but never realized.
(iv) The Green Group designation of
an emissions unit is not affected by
redesignation of the attainment status of
the area in which it is located. That is,
if a Green Group is located in an
attainment area and the area is
redesignated to nonattainment, its Green
Group designation is not affected.
Similarly, redesignation from
nonattainment to attainment does not
affect the Green Group designation.
However, if an existing Green Group
designation expires, it must re-qualify
under the requirements that are
currently applicable in the area.
(6) Setting the 10-year Green Group
emissions limit. (i) Except as provided
in paragraphs (dd)(6)(ii) through (iv) of
this section, the Green Group emissions
limit shall be established as the sum of
the baseline actual emissions (as
defined in paragraph (b)(48) of this
section) of the Green Group pollutant
for each emissions activity included in
the Green Group. When establishing the
Green Group emissions limit, for a
Green Group pollutant, a single period
of 24 consecutive months must be used
to determine the baseline actual
emissions for all existing emissions
activities. However, a different period of
24 consecutive months may be used for
each different Green Group pollutant.
Emissions associated with activities that
were permanently shut down after this
24-month period must be subtracted
from the Green Group emissions limit.
The Administrator shall specify a
reduced Green Group emissions limit(s)
(in tons/yr) in the Green Group permit
to become effective on the future
compliance date(s) of any applicable
Federal or State regulatory
requirement(s) that the Administrator is
aware of prior to issuance of the Green
Group permit.
(ii) For activities (which do not
include modifications to existing units)
on which actual construction began
after the 24-month period, in lieu of
adding the baseline actual emissions as
specified in paragraph (dd)(6)(i) of this
section, the emissions must be added to
the Green Group emissions limit in an
amount equal to the potential to emit of
the activities.
(iii) The Administrator shall establish
the Green Group emissions level by
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adjusting the total derived according to
paragraphs (dd)(6)(i) and (ii) of this
section to reflect:
(a) The application of BACT; and
(b) An additional amount of actual
emissions consistent with the growth
approved for the Green Group.
(iv) Notwithstanding the methodology
set out above in paragraphs (dd)(6)(i)
through (iii) of this section, the
Administrator shall reduce the Green
Group emissions limit and/or establish
short-term emissions limits as necessary
to meet other applicable requirements of
this section, including the requirements
of paragraphs (k) and (p).
(7) Content of the Green Group
permit. The Green Group permit must
contain the elements listed in
paragraphs (dd)(7)(i) through (xiv) of
this section and any other provisions
that the Administrator deems necessary
to implement the Green Group.
(i) The Green Group pollutant.
(ii) A description of the equipment
that comprises the Green Group,
including a description of existing
emissions activities, any authorized
physical changes or changes in method
of operation, and the common air
pollution control device. The
description must provide information
about the maximum total emissions that
will be generated by the Green Group’s
emissions activities and the associated
characteristics of the combined
emissions streams that will be ducted to
the common air pollution control
device. The description must be
sufficient to distinguish, when a change
is subsequently made in the Green
Group, whether that change was
authorized under the Green Group
permit.
(iii) A statement designating the
described equipment as a Green Group.
(iv) The Green Group emissions limit
(in terms of a 12-month total, rolled
monthly) for the group of emissions
activities included under the Green
Group.
(v) Any shorter-term emissions limits
that are necessary to safeguard ambient
air quality, as determined according to
the requirements of this section.
(vi) All emissions limitations and
work practice requirements established
to ensure that BACT is met.
(vii) The Green Group effective date
and the expiration date of the Green
Group (i.e., the Green Group effective
period). If the source owner or operator
must construct a new air pollution
control device or modify an existing
device as a result of the BACT
determination for the Green Group, the
permit may provide that the existing
emissions activities within the Green
Group are not required to meet the
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BACT emissions limitation(s) or the
Green Group emissions limit until the
new or modified air pollution control
device is in operation. (That is, such
emissions activities may continue to
meet pre-existing emissions limitations
until that time.) However, new and
modified emissions activities within the
Green Group must be subject to BACT
upon startup. In addition, the Green
Group must be subject to the Green
Group emissions limit (and associated
monitoring, recordkeeping, and
reporting requirements) beginning at the
time that the new or modified air
pollution control device is placed in
operation.
(viii) Specification in the Green Group
permit that if a major stationary source
owner or operator applies to renew a
Green Group in accordance with
paragraph (dd)(11) of this section before
the end of the effective period, then the
Green Group shall not expire at the end
of the effective period. It shall remain in
effect until a new Green Group permit
is issued by the Administrator.
(ix) A requirement that emissions
calculations for compliance purposes
must include emissions from startups,
shutdowns, and malfunctions.
(x) A requirement that, once the Green
Group expires, the major stationary
source is subject to the requirements of
paragraph (dd)(10) of this section.
(xi) The calculation procedures that
the major stationary source owner or
operator shall use to convert the
monitoring system data to monthly
emissions and annual emissions based
on a 12-month rolling total as required
by paragraph (dd)(15)(i) of this section.
(xii) A requirement that the major
stationary source owner or operator
meet all applicable requirements for
monitoring, testing, and operation in
accordance with the provisions under
paragraphs (dd)(13) and (14) of this
section.
(xiii) A requirement to retain the
records required under paragraph
(dd)(15) of this section on site. Such
records may be retained in an electronic
format.
(xiv) A requirement to submit the
reports required under paragraph
(dd)(16) of this section by the required
deadlines.
(8) Green Group effective period. The
Administrator shall specify an effective
period of 10 years. The effective period
begins upon the Green Group effective
date, which is the date that the Green
Group permit becomes effective.
(9) Reopening of the Green Group
permit. The requirements in paragraphs
(dd)(9)(i) through (iii) of this section
apply to reopening Green Group
permits.
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(i) Mandatory reopenings. During the
Green Group effective period, the
Administrator must reopen the Green
Group permit to:
(a) Correct typographical/calculation
errors made in setting the Green Group
emissions limit or reflect a more
accurate determination of emissions
used to establish this limit;
(b) Reduce the Green Group emissions
limit if the owner or operator of the
major stationary source creates
creditable emissions reductions for use
as offsets under (51.165(a)(3)(ii) of this
chapter; and
(c) Reduce the Green Group emissions
limit if the owner or operator of the
major stationary source creates
creditable emissions reductions for use
in a netting analysis under paragraph
(b)(3) of this section.
(ii) Discretionary reopenings. The
Administrator shall have discretion to
reopen the Green Group permit for the
purposes listed in paragraphs
(dd)(9)(ii)(a) through (c) of this section.
If the Administrator declines to reopen
the Green Group permit for any of these
purposes, the Green Group emissions
limit must be adjusted upon expiration
of the Green Group designation or upon
renewal of the source’s title V permit,
whichever comes first. The major
stationary source owner or operator is
responsible for compliance with any
new applicable requirements, regardless
of when the permit is reopened and
adjusted.
(a) To reduce the Green Group
emissions limit to reflect newly
applicable Federal requirements (for
example, NSPS) with compliance dates
after the Green Group effective date;
(b) To reduce the emissions limit
consistent with any other requirement,
that is enforceable as a practical matter,
and that the State may impose on the
major stationary source under the State
Implementation Plan; and
(c) To reduce the emissions limit if
the Administrator determines that a
reduction is necessary to avoid causing
or contributing to a NAAQS or PSD
increment violation, or to an adverse
impact on an air quality related value
that has been identified for a Federal
Class I area by a Federal Land Manager
and for which information is available
to the general public.
(iii) Required process. Except for the
permit reopening in paragraph
(dd)(9)(i)(a) of this section for the
correction of typographical/calculation
errors that do not increase the Green
Group emissions limit, all other
reopenings shall be carried out in
accordance with the public
participation requirements of paragraph
(q) of this section.
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(10) Expiration of a Green Group. Any
Green Group designation that is not
renewed in accordance with the
procedures in paragraph (dd)(11) of this
section shall expire at the end of its
effective period. After expiration of the
Green Group designation, the following
provisions apply:
(i) The emissions unit defined by the
Green Group remains an emissions unit
for purposes of major NSR and remains
subject to the BACT control
requirements; Green Group emissions
limit; any shorter-term emissions limits;
and monitoring recordkeeping,
reporting, and testing requirements
imposed by the Green Group permit.
(ii) The major stationary source owner
or operator shall continue to comply
with any State or Federal applicable
requirements (BACT, RACT, NSPS, etc.)
that may have applied either during or
prior to the Green Group effective
period.
(iii) Any subsequent physical change
or change in the method of operation at
the emissions unit defined by the Green
Group will be subject to PSD
requirements if such change meets the
definition of major modification in
paragraph (b)(2) of this section.
(11) Renewal of a Green Group. The
following provisions apply to renewal of
a Green Group:
(i) Required procedures. A Green
Group may be renewed through
issuance of a new major NSR permit
according to all the requirements of this
paragraph (dd) for the initial Green
Group designation.
(ii) Application deadline. A major
stationary source owner or operator
shall submit a timely application to the
Administrator to request renewal of a
Green Group. A timely application is
one that is submitted at least 6 months
prior to, but not earlier than 18 months
from, the date that the Green Group
designation would otherwise expire.
This deadline for application submittal
is to ensure that the Green Group
designation will not expire before the
Green Group is renewed. If the owner or
operator of a major stationary source
submits a complete application to renew
the Green Group within this time
period, then the Green Group shall
continue to be effective until the new
PSD permit with the renewed Green
Group is issued.
(12) Increasing a Green Group
emissions limit during its effective
period. The Administrator may increase
a Green Group emissions limit during
its effective period only if the increase
is contained in a new permit
incorporating the increase into a new
Green Group consistent with the
requirements of this section.
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(13) Monitoring requirements for
Green Group emissions limitations.
(i) General requirements.
(a) Each Green Group permit must
contain enforceable requirements for the
monitoring system that accurately
determines, in terms of mass per unit of
time, emissions of the Green Group
pollutant from the emissions activities
under the Green Group. Any monitoring
system authorized for use in the Green
Group permit must be based on sound
science and meet generally acceptable
scientific procedures for data quality
and manipulation. Additionally, the
information generated by such system
must meet minimum legal requirements
for admissibility in a judicial
proceeding to enforce the Green Group
permit.
(b) The Green Group monitoring
system must employ one or more of the
four general monitoring approaches
meeting the minimum requirements set
forth in paragraphs (dd)(13)(ii)(a)
through (d) of this section and must be
approved by the Administrator.
(c) Notwithstanding paragraph
(dd)(13)(i)(b) of this section, you may
also employ an alternative monitoring
approach that meets paragraph
(dd)(13)(i)(a) of this section if approved
by the Administrator.
(d) Failure to use a monitoring system
that meets the requirements of this
section renders the Green Group
invalid.
(ii) Minimum performance
requirements for approved monitoring
approaches. The following are
acceptable general monitoring
approaches when conducted in
accordance with the minimum
requirements in paragraphs (dd)(13)(iii)
through (ix) of this section:
(a) Mass balance calculations for
activities using coatings or solvents;
(b) CEMS;
(c) CPMS or PEMS; and
(d) Emissions factors.
(iii) Mass balance calculations. An
owner or operator using mass balance
calculations to monitor the Green Group
pollutant emissions from activities
using coating or solvents shall meet the
following requirements:
(a) Provide a demonstrated means of
validating the published content of the
Green Group pollutant that is contained
in or created by all materials used in or
at the emissions activity;
(b) Assume that the emissions activity
emits all of the Green Group pollutant
that is contained in or created by any
raw material or fuel used in or at the
emissions activity, if it cannot otherwise
be accounted for in the process; and
(c) Where the vendor of a material or
fuel, which is used in or at the
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emissions activity, publishes a range of
pollutant content from such material,
the owner or operator must use the
highest value of the range to calculate
the Green Group pollutant emissions
unless the Administrator determines
there is site-specific data or a sitespecific monitoring program to support
another content within the range.
(iv) CEMS. An owner or operator
using CEMS to monitor Green Group
pollutant emissions shall meet the
following requirements:
(a) CEMS must comply with
applicable Performance Specifications
found in 40 CFR part 60, appendix B;
and
(b) CEMS must sample, analyze, and
record data at least every 15 minutes
while the emissions activity is
operating.
(v) CPMS or PEMS. An owner or
operator using CPMS or PEMS to
monitor Green Group pollutant
emissions shall meet the following
requirements:
(a) The CPMS or the PEMS must be
based on current site-specific data
demonstrating a correlation between the
monitored parameter(s) and the Green
Group pollutant emissions across the
range of operation of the emissions
activity; and
(b) Each CPMS or PEMS must sample,
analyze, and record data at least every
15 minutes, or at another less frequent
interval approved by the Administrator,
while the emissions activity is
operating.
(vi) Emissions factors. An owner or
operator using emissions factors to
monitor Green Group pollutant
emissions shall meet the following
requirements:
(a) All emissions factors shall be
adjusted, if appropriate, to account for
the degree of uncertainty or limitations
in the factors’ development;
(b) The emissions activity shall
operate within the designated range of
use for the emissions factor, if
applicable; and
(c) If technically practicable, the
owner or operator of a significant or
major emissions activity that relies on
an emissions factor to calculate Green
Group pollutant emissions shall
conduct validation through performance
testing or other scientifically valid
means approved by the Administrator to
determine a site-specific emissions
factor. Such testing or other means shall
occur within 6 months of Green Group
permit issuance.
(vii) Missing data procedures. A
source owner or operator must record
and report maximum potential
emissions without considering
enforceable emissions limitations or
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operational restrictions for an emissions
activity during any period of time that
there is no monitoring data, unless
another method for determining
emissions during such periods is
specified in the Green Group permit.
(viii) Alternative requirements.
Notwithstanding the requirements in
paragraphs (dd)(13)(iii) through (vii) of
this section, where an owner or operator
of an emissions activity cannot
demonstrate a correlation between the
monitored parameter(s) and the Green
Group pollutant emissions rate at all
operating points of the emissions
activity, the Administrator shall, at the
time of permit issuance:
(a) Establish default value(s) for
determining compliance with the Green
Group emissions limit based on the
highest potential emissions reasonably
estimated at such operating point(s); or
(b) Determine that operation of the
emissions activity during operating
conditions when there is no correlation
between monitored parameter(s) and the
Green Group pollutant emissions is a
violation of the Green Group emissions
limit.
(ix) Re-validation. All data used to
establish the Green Group pollutant
emissions must be re-validated through
performance testing or other
scientifically valid means approved by
the Administrator. Such testing must
occur at least once every 5 years after
issuance of the Green Group.
(14) Additional monitoring
requirements for BACT. The permit
shall also require the owner or operator
with a Green Group to monitor,
measure, and record data sufficient to
determine whether:
(i) The emissions reduction measures
(including the Green Group air
pollution control device) meet the
emissions limitations and/or work
practice requirements adopted in
conjunction with BACT; and
(ii) The demonstrated capacity of the
Green Group air pollution control
device was exceeded by the emissions
stream(s) directed to it at any time
during the reporting period. The
capacity of the control device is
considered exceeded if the
characteristics of the emissions stream
entering the device are outside the range
for which it has been demonstrated that
the device can achieve BACT, absent
valid monitoring data (from a
continuous monitoring system or other
monitoring approach approved for such
use by the Administrator) showing
compliance with BACT at the new
operating level. A period of exceedance
is considered a deviation for purposes of
recordkeeping and reporting.
(15) Recordkeeping requirements.
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(i) Records to determine compliance.
The Green Group permit shall require
an owner or operator to retain a copy of
all records necessary to determine
compliance with any requirement of
paragraph (dd) of this section and of the
Green Group permit, including a
determination of each emissions
activity’s 12-month rolling total
emissions, for 5 years from the date of
such record.
(ii) Other records. The Green Group
permit shall require an owner or
operator to retain a copy of the
following records for the duration of the
Green Group effective period plus 5
years:
(a) A copy of the Green Group permit
application and any applications for
revisions to the Green Group permit;
and
(b) Each annual certification of
compliance pursuant to title V and the
data relied on in certifying the
compliance.
(16) Reporting and notification
requirements. The owner or operator
shall submit semi-annual monitoring
reports and prompt deviation reports to
the Administrator in accordance with
the applicable title V operating permit
program. The reports shall meet the
requirements in paragraphs (dd)(16)(i)
through (iii) of this section.
(i) Semi-annual report. The semiannual report shall be submitted to the
Administrator within 30 days of the end
of each reporting period. This report
shall contain the information required
in paragraphs (dd)(16)(i)(a) through (g)
of this section.
(a) The identification of owner and
operator and the permit number.
(b) Total annual emissions (tons per
year) from the emissions activities
included under the Green Group, based
on a 12-month rolling total for each
month in the reporting period recorded
pursuant to paragraph (dd)(15)(i) of this
section.
(c) All data relied upon, including,
but not limited to, any Quality
Assurance or Quality Control data, in
calculating the monthly and annual
Green Group pollutant emissions.
(d) A list of any emissions activities
included under the Green Group that
were added during the preceding 6month period.
(e) The number, duration, and cause
of any deviations or monitoring
malfunctions (other than the time
associated with zero and span
calibration checks), and any corrective
action taken.
(f) A notification of a shutdown of any
monitoring system, whether the
shutdown was permanent or temporary,
the reason for the shutdown, the
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anticipated date that the monitoring
system will be fully operational or
replaced with another monitoring
system, and whether the emissions
activity monitored by the monitoring
system continued to operate, and the
calculation of the emissions of the
pollutant or the number determined by
the method included in the permit, as
provided by paragraph (dd)(13)(vii) of
this section.
(g) A signed statement by the
responsible official (as defined by the
applicable title V operating permit
program) certifying the truth, accuracy,
and completeness of the information
provided in the report.
(ii) Deviation report. The major
stationary source owner or operator
shall promptly submit reports of any
deviations or exceedance of the Green
Group emissions limit or emissions
reduction requirement (e.g., BACT
limit), including periods where no
monitoring is available. A report
submitted pursuant to § 70.6(a)(3)(iii)(B)
of this chapter shall satisfy this
reporting requirement. The deviation
reports shall be submitted within the
time limits prescribed by the applicable
program implementing
§ 70.6(a)(3)(iii)(B) of this chapter. The
reports shall contain the following
information:
(a) The identification of owner and
operator and the permit number;
(b) The Green Group requirement that
experienced the deviation or that was
exceeded;
(c) Emissions resulting from the
deviation or the exceedance; and
(d) A signed statement by the
responsible official (as defined by the
applicable title V operating permit
program) certifying the truth, accuracy,
and completeness of the information
provided in the report.
(iii) Re-validation results. The owner
or operator shall submit to the
Administrator the results of any revalidation test or method within 3
months after completion of such test or
method.
(17) Transition requirements. The
Administrator may not issue a Green
Group permit that does not comply with
the requirements in paragraphs (dd)(1)
through (17) of this section or their
equivalent after [EFFECTIVE DATE OF
FINAL RULE]. The Administrator may
supersede any Green Group permit that
was established prior to [EFFECTIVE
DATE OF FINAL RULE] with a Green
Group permit that complies with the
requirements of paragraphs (dd)(1)
through (17) of this section.
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§ 70.5
PART 70—[AMENDED]
6. The authority citation for part 70
continues to read as follows:
Authority: 42 U.S.C. 7401, et seq.
7. Section 70.2 is amended by adding
definitions of ‘‘Alternative operating
scenario (AOS)’’ and ‘‘Approved
replicable methodology (ARM)’’ in
alphabetical order, to read as follows:
§ 70.2
Definitions.
*
*
*
*
*
Alternative operating scenario (AOS)
means a scenario authorized in a part 70
permit that involves a physical or
operational change at the part 70 source
for a particular emissions unit, and that
subjects the unit to one or more
applicable requirements that differ from
those applicable to the emissions unit
prior to implementation of the change or
renders inapplicable one or more
requirements previously applicable to
the emissions unit prior to
implementation of the change.
*
*
*
*
*
Approved replicable methodology
(ARM) means part 70 permit terms that:
(1) Specify a protocol which is
consistent with and implements an
applicable requirement, or requirement
of this part, such that the protocol is
based on sound scientific/mathematical
principles and provides reproducible
results using the same inputs; and
(2) Require the results of that protocol
to be used for assuring compliance with
such applicable requirement or
requirement of this part, including
where an ARM is used for determining
applicability of a specific requirement to
a particular change.
*
*
*
*
*
8. Section 70.4 is amended by revising
paragraph (d)(3)(xi) to read as follows:
§ 70.4 State program submittals and
transition.
*
*
*
*
*
(d) * * *
(3) * * *
(xi) Approval of AOSs. The program
submittal must include provisions to
insure that AOSs requested by the
source and approved by the permitting
authority are included in the part 70
permit pursuant to § 70.6(a)(9).
*
*
*
*
*
9. Section 70.5 is amended as follows:
a. By revising paragraph (c)(2);
b. By revising paragraph (c)(3)(iii);
c. By revising paragraph (c)(7);
d. By adding paragraph (c)(8)(ii)(D);
and
e. By adding paragraph (c)(8)(iii)(D).
The additions and revisions read as
follows:
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52259
Permit applications.
*
*
*
*
*
(c) * * *
(2) A description of the source’s
processes and products (by Standard
Industrial Classification Code) including
those associated with any AOS
identified by the source.
(3) * * *
(iii) Emissions rate in tpy and in such
terms as are necessary to establish
compliance consistent with the
applicable standard reference test
method. For emissions units subject to
an emissions cap, tpy can be reported as
part of the aggregate emissions
associated with the cap, except where
more specific information is needed to
determine an applicable requirement.
*
*
*
*
*
(7) Additional information as
determined to be necessary by the
permitting authority to define AOSs
identified by the source pursuant to
§ 70.6(a)(9) of this part or to define
permit terms and conditions
implementing any AOS under
§ 70.6(a)(9) or implementing
§ 70.4(b)(12) or § 70.6(a)(10) of this part.
The permit application shall include
documentation demonstrating that the
source has obtained all authorization(s)
required under the applicable
requirements relevant to any proposed
AOSs, or a certification that the source
has submitted all relevant materials,
including permit application(s) to the
appropriate permitting authority, for
obtaining such authorization(s).
(8) * * *
(ii) * * *
(D) For applicable requirements
associated with an AOS, a statement
that the source will meet such
requirements upon implementation of
the AOS. If an AOS implicates an
applicable requirement that will become
effective during the permit term, a
statement that the source will meet such
requirements on a timely basis.
(iii) * * *
(D) For applicable requirements
associated with an AOS, a statement
that the source will meet such
requirements upon implementation of
the AOS. If an AOS involves an
applicable requirement that will become
effective during the permit term, a
statement that the source will meet such
requirements on a timely basis. A
statement that the source will meet in a
timely manner applicable requirements
that become effective during the permit
term will satisfy this provision, unless
a more detailed schedule is expressly
required by the applicable requirement.
*
*
*
*
*
10. Section 70.6 is amended by
revising paragraphs (a)(1) introductory
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text, (a)(3)(iii)(A), and (a)(9) to read as
follows:
jlentini on PROD1PC65 with PROPOSALS2
§ 70.6
PART 71—[AMENDED]
11. The authority citation for part 71
continues to read as follows:
Permit content.
(a) * * *
(1) Emissions limitations and
standards, including those operational
requirements and limitations that assure
compliance with all applicable
requirements at the time of permit
issuance, such as ARMs.
*
*
*
*
*
(3) * * *
(iii) * * *
(A) Submittal of reports of any
required monitoring at least every 6
months. All instances of deviations from
permit requirements must be clearly
identified in such reports, and the
reports must identify the AOSs and
relevant ARMs implemented during the
reporting period. All required reports
must be certified by a responsible
official consistent with § 70.5(d) of this
part.
*
*
*
*
*
(9) Terms and conditions for
reasonably anticipated alternative
operating scenarios (AOSs) identified by
the source in its application as approved
by the permitting authority. Such terms
and conditions:
(i) Shall require the source,
contemporaneously with making a
change from one operating scenario to
another, to record in a log at the
permitted facility a record of the AOS
under which it is operating. The log
shall include a description of the change
that triggered the AOS; the emissions
unit(s) included in the AOS; the
applicable requirements and other
permit terms and conditions that apply
to the AOS; and the date the source
began to operate the AOS;
(ii) May extend the permit shield
described in paragraph (f) of this section
to all terms and conditions under each
such AOS; and
(iii) Must ensure that the terms and
conditions of each AOS meet all
applicable requirements and the
requirements of this part. The permit
terms must include a description of the
emissions units, the anticipated
changes, and the applicable
requirements included in the AOS, and
must describe how the source will
comply with such requirements. The
permitting authority shall not approve
an AOS into the part 70 permit until the
source has obtained all authorizations
required under any applicable
requirement relevant to that AOS.
*
*
*
*
*
VerDate Aug<31>2005
18:46 Sep 11, 2007
Jkt 211001
Authority: 42 U.S.C. 7401, et seq.
12. Section 71.2 is amended by
adding definitions of ‘‘Alternative
operating scenario (AOS)’’ and
‘‘Approved replicable methodology
(ARM)’’ in alphabetical order, to read as
follows:
§ 71.2
Definitions.
*
*
*
*
*
Alternative operating scenario (AOS)
means a scenario authorized in a part 71
permit that involves a physical or
operational change at the part 71 source
for a particular emissions unit, and that
subjects the unit to one or more
applicable requirements that differ from
those applicable to the emissions unit
prior to implementation of the change or
renders inapplicable one or more
requirements previously applicable to
the emissions unit prior to
implementation of the change.
*
*
*
*
*
Approved replicable methodology
(ARM) means part 71 permit terms that:
(1) Specify a protocol which is
consistent with and implements an
applicable requirement, or requirement
of this part, such that the protocol is
based on sound scientific/mathematical
principles and provides reproducible
results using the same inputs; and
(2) Require the results of that protocol
to be used for assuring compliance with
such applicable requirement or
requirement of this part, including
where an ARM is used for determining
applicability of a specific requirement to
a particular change.
*
*
*
*
*
13. Section 71.5 is amended as
follows:
a. By revising paragraph (c)(2);
b. By revising paragraph (c)(3)(iii);
c. By revising paragraph (c)(7);
d. By adding paragraph (c)(8)(ii)(D);
and
e. By adding paragraph (c)(8)(iii)(D).
The additions and revisions read as
follows:
§ 71.5
Permit applications.
*
*
*
*
*
(c) * * *
(2) A description of the source’s
processes and products (by Standard
Industrial Classification Code) including
those associated with any AOS
identified by the source.
(3) * * *
(iii) Emissions rates in tpy and in
such terms as are necessary to establish
compliance consistent with the
PO 00000
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Fmt 4701
Sfmt 4702
applicable standard reference test
method. For emissions units subject to
an emissions cap, tpy can be reported as
part of the aggregate emissions
associated with the cap, except where
more specific information is needed to
determine an applicable requirement.
*
*
*
*
*
(7) Additional information as
determined to be necessary by the
permitting authority to define AOSs
identified by the source pursuant to
§ 71.6(a)(9) or to define permit terms
and conditions implementing any AOS
under § 71.6(a)(9) or implementing
§ 71.6(a)(10) or § 71.6(a)(13). The permit
application shall include
documentation demonstrating that the
source has obtained all authorization(s)
required under the applicable
requirements relevant to any proposed
AOSs, or a certification that the source
has submitted all relevant materials,
including permit application(s) to the
appropriate permitting authority, for
obtaining such authorization(s).
(8) * * *
(ii) * * *
(D) For applicable requirements
associated with an AOS, a statement
that the source will meet such
requirements upon implementation of
the AOS. If an AOS implicates an
applicable requirement that will become
effective during the permit term, a
statement that the source will meet such
requirements on a timely basis.
(iii) * * *
(D) For applicable requirements
associated with an AOS, a statement
that the source will meet such
requirements upon implementation of
the AOS. If an AOS includes an
applicable requirement that will become
effective during the permit term, a
statement that the source will meet such
requirements on a timely basis. A
statement that the source will meet in a
timely manner applicable requirements
that become effective during the permit
term will satisfy this provision, unless
a more detailed schedule is expressly
required by the applicable requirement.
*
*
*
*
*
14. Section 71.6 is amended by
revising paragraphs (a)(1) introductory
text, (a)(3)(iii)(A), and (a)(9) to read as
follows:
§ 71.6
Permit content.
(a) * * *
(1) Emissions limitations and
standards, including those operational
requirements and limitations that assure
compliance with all applicable
requirements at the time of permit
issuance, such as ARMs.
*
*
*
*
*
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jlentini on PROD1PC65 with PROPOSALS2
(3) * * *
(iii) * * *
(A) Submittal of reports of any
required monitoring at least every 6
months. All instances of deviations from
permit requirements must be clearly
identified in such reports, and the
reports must identify the AOSs and
relevant ARMs implemented during the
reporting period. All required reports
must be certified by a responsible
official consistent with § 71.5(d).
*
*
*
*
*
(9) Terms and conditions for
reasonably anticipated alternative
operating scenarios (AOSs) identified by
the source in its application as approved
VerDate Aug<31>2005
18:46 Sep 11, 2007
Jkt 211001
by the permitting authority. Such terms
and conditions:
(i) Shall require the source,
contemporaneously with making a
change from one operating scenario to
another, to record in a log at the
permitted facility a record of the AOS
under which it is operating. The log
shall include a description of the change
that triggered the AOS; the emissions
unit(s) included in the AOS; the
applicable requirements and other
permit terms and conditions that apply
to the AOS; and the date the source
began to operate the AOS;
(ii) May extend the permit shield
described in paragraph (f) of this section
to all terms and conditions under each
such AOS; and
PO 00000
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Fmt 4701
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52261
(iii) Must ensure that the terms and
conditions of each AOS meet all
applicable requirements and the
requirements of this part. The permit
terms must include a description of the
emissions units, the anticipated
changes, and the applicable
requirements included in the AOS, and
must describe how the source will
comply with such requirements. The
permitting authority shall not approve
an AOS into the part 71 permit until the
source has obtained all authorizations
required under any applicable
requirement relevant to that AOS.
*
*
*
*
*
[FR Doc. E7–17418 Filed 9–11–07; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 72, Number 176 (Wednesday, September 12, 2007)]
[Proposed Rules]
[Pages 52206-52261]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E7-17418]
[[Page 52205]]
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Part II
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Parts 51, 52, 70, and 71
Operating Permit Programs and Prevention of Significant Deterioration
(PSD) and Nonattainment New Source Review (NSR); Flexible Air
Permitting Rule; Proposed Rule
Federal Register / Vol. 72, No. 176 / Wednesday, September 12, 2007 /
Proposed Rules
[[Page 52206]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 51, 52, 70, and 71
[EPA-HQ-OAR-2004-0087, FRL-8462-9]
RIN 2060-AM45
Operating Permit Programs and Prevention of Significant
Deterioration (PSD) and Nonattainment New Source Review (NSR); Flexible
Air Permitting Rule
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: We are proposing to revise the regulations governing State and
Federal operating permit programs required by title V of the Clean Air
Act (CAA or the Act) and the New Source Review (NSR) programs required
by parts C and D of title I of the Act. These proposed actions are
based, in large part, on the lessons learned through EPA's pilot
experience in which EPA worked closely with States and certain sources
subject to title V permitting requirements to develop flexible air
permitting approaches that provide greater operational flexibility and,
at the same time, ensure environmental protection and compliance with
applicable laws.
In pilot permits, increased flexibility is primarily achieved
through advance approvals under NSR and alternative operating scenarios
(AOSs). The proposed revisions clarify how this can often be done in
the existing regulatory framework of the operating permit programs. The
proposed revisions also add major NSR requirements for Green Groups,
which allow future changes to occur within a group of emissions
activities, provided that they are ducted to a common air pollution
control device which is determined to meet ``best available control
technology'' (BACT) or ``lowest achievable emission rate'' (LAER), as
applicable and that they are determined to comply with all relevant
ambient requirements.
DATES: Comments. Written comments must be received on or before
November 13, 2007. Under the Paperwork Reduction Act, comments on the
information collection provisions must be received by OMB on or before
October 12, 2007.
Public Hearing. If anyone contacts EPA requesting to speak at a
public hearing by October 2, 2007, we will hold a public hearing
approximately 30 days after publication in the Federal Register.
Additional information about the hearing would be published in a
subsequent Federal Register notice.
ADDRESSES: Comments. Submit your comments, identified by Docket ID No.
EPA-HQ-OAR-2004-0087, by one of the following methods:
https://www.regulations.gov: Follow the on-line
instructions for submitting comments.
E-mail: a-and-r-Docket@epa.gov.
Fax: (202) 566-9744.
Mail: Environmental Protection Agency, EPA Docket Center
(EPA/DC), Air and Radiation Docket, Mail Code 2822T, 1200 Pennsylvania
Avenue, NW., Washington, DC 20460. Please include two copies. In
addition, please mail a copy of your comments on the information
collection provisions to the Office of Management and Budget (OMB),
Attn: Desk Officer for EPA, 725 17th St., NW., Washington, DC 20503.
Hand Delivery: EPA Docket Center, (Air Docket), U.S.
Environmental Protection Agency, Room 3334, 1301 Constitution Ave.,
NW., Washington, DC. Such deliveries are only accepted during the
Docket's normal hours of operation, and special arrangements should be
made for deliveries of boxed information.
Instructions: Direct your comments to Docket ID No. EPA-HQ-OAR-
2004-0087. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
www.regulations.gov, including any personal information provided,
unless the comment includes information claimed to be Confidential
Business Information (CBI) or other information whose disclosure is
restricted by statute. Do not submit information that you consider to
be CBI or otherwise protected through www.regulations.gov or e-mail.
The www.regulations.gov Web site is an ``anonymous access'' system,
which means EPA will not know your identity or contact information
unless you provide it in the body of your comment. If you send an e-
mail comment directly to EPA without going through www.regulations.gov,
your e-mail address will be automatically captured and included as part
of the comment that is placed in the public docket and made available
on the Internet. If you submit an electronic comment, EPA recommends
that you include your name and other contact information in the body of
your comment and with any disk or CD-ROM you submit. 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. Electronic
files should avoid the use of special characters, any form of
encryption, and be free of any defects or viruses. For additional
instructions on submitting comments, go to I C & D of the SUPPLEMENTARY
INFORMATION section of this document.
Docket: All documents in the docket are listed in the index at
www.regulations.gov. Although listed in the index, some information is
not publicly available, i.e., CBI or other information whose disclosure
is restricted by statute. Certain other material, such as copyrighted
material, is not placed on the Internet and will be publicly available
only in hard copy form. Publicly available docket materials are
available either electronically in www.regulations.gov or in hard copy
at the EPA Docket Center (Air Docket), EPA West, Room 3334, 1301
Constitution Ave., NW., 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: For issues concerning advance
approvals and AOSs, contact Michael Trutna, Air Quality Policy Division
(C504-01), U.S. Environmental Protection Agency, Research Triangle
Park, NC 27711; telephone (919) 541-5345, fax number (919) 541-4028; or
electronic mail at trutna.mike@epa.gov.
For issues concerning ARMs and EPA's pilot permits, contact David
Beck, Office of Policy, Economics, and Innovation, Innovative Pilots
Division (C304-05), U.S. Environmental Protection Agency, Research
Triangle Park, NC 27711; telephone (919) 541-5421, fax number (919)
541-2664; or electronic mail at beck.david@epa.gov.
For issues relating to monitoring, recordkeeping, and reporting for
flexible air permits, contact Barrett Parker, Sector Policies and
Programs Division, Measurement Policy Group (D243-03), U.S.
Environmental Protection Agency, Research Triangle Park, NC 27711;
telephone 919-541-5635, fax number (919) 541-1039; or electronic mail
at parker.barrett@epa.gov.
For other part 70 issues, contact Juan Santiago, Operating Permits
Group, Air Quality Policy Division (C504-05), U.S. Environmental
Protection Agency, Research Triangle Park, NC 27711; telephone (919)
541-1084, fax number (919) 541-5509; or electronic mail at
santiago.juan@epa.gov.
For issues relating to Green Groups, contact Dave Painter, New
Source Review Group, Air Quality Policy Division (C504-03), U.S.
Environmental Protection Agency, Research Triangle Park, NC 27711;
telephone (919) 541-
[[Page 52207]]
5515, fax number (919) 541-5509; or electronic mail at
painter.david@epa.gov.
To request a hearing or information pertaining to a hearing on this
document, please contact Pam Long, Air Quality Policy Division, U.S.
EPA, Office of Air Quality Planning and Standards (C504-03), Research
Triangle Park, North Carolina 27711, telephone number (919) 541-0641,
facsimile number (919) 541-5509; electronic mail e-mail address:
long.pam@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. What are the regulated entities?
Entities potentially affected by these proposed actions are
facilities currently required to obtain title V permits under State,
local, tribal, or Federal operating permits programs, and State, local,
and tribal governments that are authorized by EPA to issue such
operating permits. Other entities potentially affected by this proposed
action are facilities required to obtain major NSR permits under State,
local, tribal, or Federal major NSR programs, and State, local, and
tribal governments that issue such permits pursuant to approved part 51
major NSR programs. Potentially affected sources are found in a wide
variety of industry groups. In particular, we believe based on our
experience in implementing our flexible air permit pilot program that
these groups will include, but are not limited to, the following:
------------------------------------------------------------------------
Industry group SIC a NAICS b
------------------------------------------------------------------------
Aerospace Manufacturing....... 372.............. 336411, 336412,
332912, 336411,
335413.
Automobile Manufacturing...... 371.............. 336111, 336112,
336712, 336211,
336992, 336322,
336312, 33633,
33634, 33635,
336399, 336212,
336213.
Industrial Organic Chemicals.. 286.............. 325191, 32511,
325132, 325192,
225188, 325193,
32512, 325199.
Chemical Processes............ 281.............. 325181, 325182,
325188, 32512,
325131, 325998,
331311.
Converted Paper and Paperboard 267.............. 322221, 322222,
Products. 322223, 322224,
322226, 322231,
326111, 326112,
322299, 322291,
322232, 322233,
322211.
Magnetic Tape Manufacturing... 369.............. 334613.
Petroleum Refining............ 291.............. 32411.
Other Coating Operations...... 226, 229, 251, 313311, 313312,
252, 253, 254, 314992, 33132,
267, 358, 363. 337122, 337121,
337124, 337215,
337129, 37125,
337211, 337214,
337127, 322221,
322222, 322226,
335221, 335222,
335224, 335228,
333312, 333415,
333319.
Paper Mills................... 262.............. 322121, 322122.
Pharmaceutical Manufacturing.. 283.............. 325411, 325412,
325413, 325414.
Printing and Publishing....... 275.............. 323114, 323110,
323111, 323113,
323112, 323115,
323119.
Pulp and Paper Mills.......... 262.............. 32211, 322121,
322122, 32213.
Semi-conductors............... 367.............. 334413.
Specialty Chemical Batch 282, 283, 284, 3251, 3252, 3253,
Processes. 285, 286, 287, 3254, 3255, 3256,
289, 386. 3259, except 325131
and 325181.
------------------------------------------------------------------------
a Standard Industrial Classification
b North American Industry Classification System.
B. What should I consider as I prepare my comments for EPA?
1. Submitting CBI
Do not submit this information to EPA through www.regulations.gov
or e-mail. Clearly mark the part or all of the information that you
claim to be CBI. For CBI information in a disk or CD-ROM that you mail
to EPA, mark the outside of the disk or CD-ROM as CBI and then identify
electronically within the disk or CD-ROM the specific information that
is claimed as CBI. In addition to one complete version of the comment
that includes information claimed as CBI, a copy of the comment that
does not contain the information claimed as CBI must be submitted for
inclusion in the public docket. Information so marked will not be
disclosed except in accordance with procedures set forth in 40 CFR part
2.
2. Suggestions for Preparing Your Comments
When submitting comments, remember to:
Identify the rulemaking by docket number and other
identifying information (subject heading, Federal Register date and
page number).
Follow directions. The Agency may ask you to respond to
specific questions or organize comments by referencing a Code of
Federal Regulations (CFR) part or section number.
Explain why you agree or disagree; suggest alternatives
and substitute language for your requested changes.
Describe any assumptions and provide any technical
information and/or data that you used.
If you estimate potential costs or burdens, explain how
you arrived at your estimate in sufficient detail to allow for it to be
reproduced.
Provide specific examples to illustrate your concerns, and
suggest alternatives.
Explain your views as clearly as possible, avoiding the
use of profanity or personal threats.
Make sure to submit your comments by the comment period
deadline identified.
C. 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 proposal will also be available on the WWW. Following signature by
the EPA Administrator, a copy of this notice will be posted in the
regulations and standards section of our NSR home page located at
https://www.epa.gov/nsr.
D. How Can I Find Information About a Possible Hearing?
Persons interested in presenting oral testimony should contact Pam
Long, Air Quality Policy Division (C504-03), U.S. EPA, Research
Triangle Park, NC 27711, telephone number (919) 541-0641 or e-mail
long.pam@epa.gov at least 2 days in advance of the public hearing.
Persons interested in attending the public hearing should also contact
Pam Long to verify the time, date, and location of the hearing. The
public hearing will provide interested parties the opportunity to
present data, views, or arguments concerning these proposed rules.
[[Page 52208]]
E. How is this preamble organized?
The information presented in this preamble is organized as follows:
I. General Information
A. What are the regulated entities?
B. What should I consider as I prepare my comments for EPA?
C. Where can I get a copy of this document and other related
information?
D. How can I find information about a possible hearing?
E. How is this preamble organized?
II. What is a flexible air permit and the background related to this
action?
A. What is a flexible air permit?
B. What is the statutory background?
C. What is the regulatory background relating to the proposed
revisions to parts 70 and 71?
D. What is the regulatory background relating to the proposed
revisions to parts 51 and 52?
III. What is the purpose of this action?
IV. What experience did we gain from our 12-year pilot permit
experience?
A. What were the benefits of the pilot permits?
B. What were the conclusions of the sources, permitting
authorities, and EPA about flexible permits?
C. What are EPA's recommendations for public participation in
flexible permitting?
V. What are the key elements of this proposal?
A. What are the key elements of proposed revisions to parts 70
and 71?
B. What are the key elements of proposed revisions to parts 51
and 52?
VI. What changes are we are proposing to parts 70 and 71?
A. What is our proposed definition of an AOS, and how does it
provide a source operational flexibility?
B. What information is necessary in a title V permit application
to seek approval of an AOS?
C. What terms and conditions must be included in the title V
permit for approved AOSs?
D. What are some examples of how AOSs and advance approvals can
be used to provide operational flexibility?
E. What is the process for adding or revising advance approvals,
AOSs, and ARMs in issued permits?
F. How do the proposed AOS provisions differ between parts 70
and 71?
VII. What changes are we proposing in parts 51 and 52?
A. What are the benefits of Green Groups?
B. What is a Green Group?
C. How is a Green Group designation incorporated into a title V
permit?
D. What is the legal rationale for Green Groups?
E. What are the conforming regulatory changes we must make to
implement the Green Group concept?
F. What is an example of how a Green Group might be used in
combination with a title V permit?
VIII. What is the effect of these proposed revisions?
A. If these proposed revisions are finalized, what are the
implications for approved part 70 programs?
B. What are the implications for NSR programs?
IX. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act (RFA)
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
II. What is a flexible air permit and the background related to this
action?
In this section, we first explain what is a flexible air permit. We
then provide an overview of the relevant statutory provisions and
describe the regulatory and other actions taken over the course of the
last decade that are relevant to this proposal.
A. What is a flexible air permit?
A flexible air permit is a title V permit that facilitates
flexible, market-responsive operations at a source through the use of
one or more permitting approaches, while ensuring equal or greater
environmental protection as achieved by conventional permits.\1\ In
particular, flexible permitting approaches allow the source, under
protection of the permit shield, to make certain types of physical and
operational changes without further review or approval by the
permitting authority. One approach includes, for example, obtaining
advance approval for anticipated changes (such as through a minor NSR
action), incorporating the advance approval into the title V permit,
and adding terms in the title V permit as necessary to assure
compliance with all other applicable requirements implicated by the
anticipated changes. Another approach is to establish one or more
alternative operating scenarios (AOSs) in a title V permit to allow
existing emissions units the flexibility to operate in varying ways
and/or at varying rates of production, where such variations would be
subject to different applicable requirements but would not require
prior authorization (i.e., advance approval).
---------------------------------------------------------------------------
\1\ We first addressed the concept of a flexibile air permit in
May 1991. See 56 FR 21712, 21748 (May 10, 1991).
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For more than a decade, we participated in a pilot flexible air
permitting program with certain title V sources and permitting
authorities through which we tested and evaluated various permitting
approaches that afford operational flexibility. The lessons learned
through the pilot program, in part, served as the basis for our
adoption of the plantwide applicability limitation (PAL) provisions of
the 2002 NSR Improvement rule. They also serve as a basis for this
rule, where we seek to build upon existing regulatory provisions that
afford operational flexibility. We believe that the flexible permitting
approaches in this proposed rulemaking provide a path forward for
sources to more effectively and proactively manage their title V and
NSR permitting obligations, while ensuring environmental protection.
B. What is the statutory background?
There are two aspects of the CAA that are relevant to this proposed
rule: title V and parts C and D of title I of the Act. In 1990,
Congress promulgated title V and established the operating permit
program. That program requires certain stationary sources to obtain
operating permits as a mechanism for gathering all applicable
requirements of the Act for each affected source into one comprehensive
document.\2\ See H.R. Conference Report No. 101-952, reprinted in
U.S.C.C.A.N. 3867, 3877 (1990).
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\2\ ``Applicable requirements'' is a term that is used in title
V. The EPA has defined the term to include, among other things,
State implementation plan (SIP) rules, the terms and conditions of
preconstruction permits issued under a SIP-approved NSR program, and
requirements pursuant to the new source performance standards
(NSPS), national emission standards for hazardous air pollutants
(NESHAP), and Acid Rain Programs. See 40 CFR 70.2.
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One of the key purposes of the title V operating permit program is
to enable the source, the State or local permitting authority, EPA, and
the public to gain a better understanding of the requirements of the
Act to which the source is subject. The ability to assess and achieve
compliance with the law is improved by virtue of having one
comprehensive operating permit containing all applicable requirements
for a source. The title V permit program does not impose new
substantive air quality control requirements. It does, however, require
that fees be imposed on sources and that certain procedural measures be
followed, especially with respect to determining compliance with
applicable requirements. See, e.g., CAA sections 502(b)(3), 503(b)(2),
and 504(a).
[[Page 52209]]
The Act affirms that State and local governments have primary
responsibility for air quality. See CAA section 101(a)(3). Title V
vests primary responsibility for issuing operating permits with State
and local governments. See CAA section 502. Congress required EPA to
promulgate regulations establishing the minimum elements of a title V
operating permits program. See CAA section 502(b) (articulating ten
minimum elements for State programs). In establishing such minimum
elements, Congress directed that EPA develop ``[a]dequate, streamlined,
and reasonable procedures'' for processing and reviewing permit
applications and for the expeditious review of permit actions. See CAA
section 502(b)(6).
As explained below, EPA promulgated regulations establishing the
minimum requirements for a State operating permit program in 1992.
These regulations are codified at 40 CFR part 70 and are often
referenced as ``part 70.'' In addition to requiring EPA to establish
the minimum elements for the operating permits program, Congress
required each State to develop and submit to EPA for approval an
operating permit program that meets the requirements of the Act and
part 70. See CAA section 502(d)(1). In areas that do not have an
approved State, local, or tribal title V program, EPA administers the
operating permit program as a Federal program pursuant to regulations
set out in 40 CFR part 71. See CAA section 502(d)(3). Title V requires
that each operating permit contain terms sufficient to assure
compliance with all applicable air requirements. See CAA section
504(a).
The other parts of the Act relevant to this rule include part C,
entitled ``Prevention of Significant Deterioration of Air Quality''
(typically referred to as ``PSD''), and part D, entitled ``Plan
Requirements for Nonattainment Areas'' (typically referred to as
``nonattainment major NSR''), of title I of the Act. See CAA sections
160 through 169B (part C) and 171 through 193 (part D). These parts
together are commonly referred to as the major NSR program. This
program is a preconstruction review and permitting program applicable
to new or modified major stationary sources of air pollutants regulated
under the Act. The implementing regulations for the program are
contained in 40 CFR 51.165, 51.166, 52.21, 52.24, and part 51, appendix
S.
The PSD provisions apply to new major sources and to major
modifications at existing major sources for pollutants where the area
in which the source is located is in attainment or unclassifiable with
the national ambient air quality standards (NAAQS). A source that is
subject to PSD must install BACT and perform an air quality analysis
and an additional impacts analysis, and there must be an opportunity
for public participation. See CAA section 165(a). The BACT is an
emissions limitation that is based on the maximum degree of control
that can be achieved, as determined on a case-by-case basis for each
source considering energy, environmental, and economic impacts. See CAA
section 169(3); 40 CFR 51.166(b)(12), 52.21(b)(12), and
51.165(a)(1)(xl). The source's air quality analysis must demonstrate
that the source will not cause or contribute to a violation of any
NAAQS or any maximum allowable increase in ambient concentration either
for a Class I area or as established under the PSD program (typically
referred to as ``PSD increments''). See CAA section 165(a)(3).
Nonattainment major NSR applies to new major sources and to major
modifications at existing major sources for pollutants where the area
in which the source is located is not in attainment with the NAAQS.\3\
Nonattainment major NSR requires the source to comply with lowest
achievable emission rate (``LAER'') and to obtain sufficient emissions
offsets, and there must be an opportunity for public involvement. See
CAA section 173(a); 40 CFR 51.161. The LAER is determined for each
source to reflect the more stringent of the following: (1) The most
stringent emissions limitation that is contained in any State
implementation plan (SIP) for that type of source (if achievable for
the proposed source), or (2) the most stringent emissions limitation
that is achieved in practice for that type of source. See CAA section
171(3); 40 CFR 51.165(a)(1)(xiii).\4\
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\3\ ``Major stationary source'' is defined at 40 CFR
51.165(a)(1)(iv), 51.166(b)(1), and 52.21(b)(1), and ``major
modification'' is defined at 40 CFR 51.165(a)(1)(v), 51.166(b)(2),
and 52.21(b)(2).
\4\ This is a section 307(d) rulemaking. See CAA section
307(d)(1)(J) (addressing regulations under part C of Subchapter I)
and 307(d)(1)(V) (authorizing the Administrator to designate any
action a 307(d) rulemaking).
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In addition to a major NSR program, States are required to have
``minor'' NSR programs, which apply to new and modified sources that do
not meet the emissions thresholds for major NSR. See section
110(a)(2)(C) of the Act. The minor NSR program is part of a State's
implementation plan and is designed to ensure that the construction or
modification of an affected source does not violate any portion of the
SIP and does not interfere with the attainment of the NAAQS or cause
the exceedance of any applicable PSD increments.
C. What is the regulatory background relating to the proposed revisions
to parts 70 and 71?
This proposed rule addresses certain permitting mechanisms for
providing operational flexibility. The concept of operational
flexibility is not a new one. In July 1992, under the authority of
title V of the Act, we finalized the part 70 State operating permit
program regulations.\5\ See 57 FR 32250 (July 21, 1992); 40 CFR part
70. Those regulations include operational flexibility provisions, one
of which is the AOS provision found at 40 CFR 70.6(a)(9). It is this
provision that is the primary subject of these proposed revisions.\6\
This section 40 CFR 70.6(a)(9) generally provides that any permit
issued under part 70 must include terms and conditions for reasonably
anticipated operating scenarios approved by the permitting authority.
EPA promulgated 40 CFR 70.6(a)(9) pursuant to the authority of section
502(b)(6) of the CAA, which directs that operating permit programs
include ``[a]dequate, streamlined, and reasonable procedures'' for
processing and reviewing permit applications and for the expeditious
review of permit actions.
---------------------------------------------------------------------------
\5\ In the 1990's, we proposed certain clarifications and
modifications to the part 70 regulations, none of which were ever
finalized. See generally 60 FR 45529 (Aug. 31, 1995), 59 FR 44460
(Aug. 29, 1994). In those proposals, among other things, we
discussed the concept of ``advance NSR'' in relation to AOSs, and
proposed a definition for ``alternative operating scenarios.''
\6\ The EPA included other operational flexibility provisions in
the final part 70 regulations, including 40 CFR 70.4(b)(12), (b)(14)
and (b)(15), which implement section 502(b)(10) of the Act. This
proposed rule does not address these provisions.
---------------------------------------------------------------------------
In the final part 70 rule, we emphasized the importance of 40 CFR
70.6(a)(9), noting that a permit that contains approved AOSs ``will be
a more complete representation of the operation at the permitted
facility.'' See 57 FR 32276. We also explained that once a flexible air
permit with approved AOSs is issued, the need for additional permit
modifications will be substantially reduced since the permit will
already contain appropriate terms and conditions to accommodate the
approved operating scenarios. In the final part 70 rule, we did not
place any restrictions on the types of operations that could qualify as
a reasonably anticipated operating scenario.\7\
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\7\ The Federal operating permit program at part 71 addresses
reasonably anticipated operating scenarios in the same fashion as
part 70. See 40 CFR 71.6(a)(9). These proposed revisions affect both
parts 70 and 71 and the revisions that we propose to each part are
virtually identical. For ease of reference, this preamble discussion
refers to the part 70 provisions. The discussion, of course, applies
equally to the part 71 program revisions proposed. Section numbers
given for the part 70 rules correspond directly to the analogous
sections in part 71. The term ``title V permit'' refers to permits
issued under either part 70 or part 71.
---------------------------------------------------------------------------
[[Page 52210]]
Shortly after we finalized the part 70 State operating permit
program, we initiated a pilot title V permit program with interested
States, and our program continues to the present. See section IV of
this preamble for more discussion. Companies participating in the pilot
program sought to reduce the cost, time, and delays associated with a
permit revision for each operational change at a facility. We and the
States sought to increase the sources' operational flexibility, while
assuring compliance with applicable requirements, ensuring
environmental protection, and facilitating P2. These pilots typically
allowed for both changes to operations of existing emissions units and
the addition of entirely new emissions units, provided that the changes
were sufficiently well described in the permit application so that the
permitting authority could confirm that all applicable requirements
were identified and that the permit contained terms and conditions
assuring compliance with all applicable requirements.\8\
---------------------------------------------------------------------------
\8\ In implementing the pilot projects, EPA and other permitting
authorities sometimes imposed certain constraints in the permits for
advance approvals and AOSs beyond those expressly contained in
applicable requirements or part 70. These additional constraints
varied and were designed to provide permitting authorities the
opportunity to gain experience with different flexible permitting
approaches. Some of these constraints were anticipated to be removed
at the time of permit renewal in the next version of the permit.
---------------------------------------------------------------------------
To evaluate the flexible pilot permits program, we conducted a
thorough review of six of the pilot permits for which at the time there
was significant implementation experience.\9\ We reviewed on-site
records to track utilization of the flexible permit provisions,
assessed how well the permits worked, evaluated total emissions
reductions achieved, and analyzed the economic benefits associated with
the permits. Overall, we found that significant environmental benefits
had occurred for each of the permits reviewed. At the time of the
evaluation, each of the sources had achieved 25- to 80-percent
reductions in actual plantwide emissions or emissions per unit of
production. We made a series of findings based on our evaluation of the
permits. See ``Evaluation of the Implementation Experience with
Innovative Air Permits'' and section IV of this preamble, which
summarizes the findings of this study.\10\
---------------------------------------------------------------------------
\9\ See ``Evaluation of the Implementation Experience with
Innovative Air Permits.'' A copy of this report is located in the
docket for this rulemaking, or can be accessed at https://
www.epa.gov/ttn/oarpg/t5/memoranda/iap_eier.pdf.
\10\ In August 2000, based in large part on the experience we
gained through the pilot permit program, we issued a draft guidance
document called White Paper Number 3, on which we solicited comment.
See White Paper Number 3, 64 FR 49803 (Aug. 15, 2000). That draft
guidance addressed various flexible permitting approaches, including
the use of the reasonably anticipated AOS provision of 40 CFR
70.6(a)(9), Clean Buildings, and PALs. We received comments on the
proposed rules and draft guidance and, in fashioning this proposal,
considered those comments that addressed advance approval and AOSs
as contained in 40 CFR 70.6(a)(9). As explained further below, we
propose a definition of ``alternative operating scenario'' and
certain other revisions to the part 70 regulations. We also propose
revisions to parts 51 and 52 that provide for Green Groups.
---------------------------------------------------------------------------
D. What is the regulatory background relating to the proposed revisions
to parts 51 and 52?
Based on our pilot permit evaluation and our 1996 proposed
modifications to the major NSR program, in December 2002, we finalized
the NSR Improvement rule. In that rule, we promulgated regulations for
PALs in response to comments received on draft White Paper Number 3. As
explained in the preamble to the December 2002 final rule, a PAL is an
alternative approach for determining NSR applicability on a plantwide
basis. Using PALs will allow sources ``to respond rapidly to market
changes,'' and will ``benefit the public and the environment.'' See 67
FR 80206. Specifically, sources with PALs can make changes without
triggering the major NSR preconstruction permitting requirements,
provided such changes remain below the limit established in their PAL
and do not otherwise violate the requirements of the PAL. A PAL is an
important technique that is oftentimes used in tandem with flexible
permitting approaches such as advance approvals and AOSs as described
more fully in this proposal.
The major NSR program applies to ``major stationary sources,''
which include sources whose emissions exceed certain thresholds
established in the statute, and to ``major modifications'' at those
sources, which are modifications that exceed certain significance
levels established in EPA's regulations. Under minor NSR, an owner or
operator applies for a permit to construct or modify a facility,
building, or other emissions unit, where the new construction or
modification does not meet the emissions thresholds for major NSR. If
the proposed construction or modification is approved, the permitting
authority issues a permit that contains emissions limits and other
appropriate terms and conditions as necessary to protect the NAAQS and
the increments and to assure consistency with the SIP.
Through our pilot experience, we found that State minor NSR
requirements are among the most important in designing a flexible air
permit for sources making frequent physical and operational changes
because, absent an up-front authorization for these changes, an
individual review and approval by the permitting authority is typically
required before the changes can be made. Any changes authorized under
minor NSR must be incorporated into the title V permit along with
permit terms as necessary to assure compliance with all applicable
requirements (for example, a MACT standard, which would be applicable
to the source in addition to the ones addressed in the advance approval
issued under minor NSR). The result is that the changes can be
implemented, under protection of the permit shield, without any further
review or approval by the permitting authority. In some cases, one or
more AOSs may be used to complement an advance approval, for example
where the source anticipates varying operation of the changed existing
emissions unit in a manner that would implicate a set of applicable
requirements different from those of the minor NSR advance approval, or
where a different control approach would not be effective until and
unless a particular change would be made to an existing emissions unit.
Given the provisions of their minor NSR programs, most of the
States in which EPA supported flexible permit pilots (``pilot States'')
believed that they could issue construction approval for a wide
spectrum of changes using certain boundary conditions established up
front in the minor NSR permit. The actual conditions needed to
accomplish this varied depending upon the requirements of the different
State minor NSR programs. A number of techniques were successfully used
in pilot permits to authorize a category of changes (i.e., a range of
possible types of changes, such as ``any of various physical changes to
the rollers, drive mechanism, and other components of the coating
section within a coating line'') under minor NSR, including application
of one or more plantwide emissions caps, designation of an entire
process building or related activities as the ``emissions unit'' for
purposes of minor NSR, and designation of an
[[Page 52211]]
existing state-of-the-art emissions capture and control system as
fulfilling State control technology requirements (where they are
applicable) for authorized changes occurring over the 5-year term of
the title V permit. Pilot States, as part of granting advance approvals
under their existing minor NSR programs, frequently required sources to
send a notice to the permitting authority contemporaneous with the
operation of any entirely new emissions unit relying upon the advance
approval.
A common technique for achieving advance approval under minor NSR
found in the pilots was the presence of one or more plantwide emissions
caps. These caps serve to limit the maximum aggregate emissions
associated with the anticipated changes so as to protect relevant
ambient standards and increments and to facilitate an advance approval
of a wide spectrum of changes under minor NSR. They also serve to limit
the potential to emit (PTE) of the source below certain applicability
thresholds in order to prevent implication of otherwise potentially
applicable requirements (e.g., major NSR) or to function as a PAL (in
the case of an existing major stationary source).
III. What is the purpose of this action?
The Agency has learned a great deal over the past decade through
its pilot permit program. In light of that experience, the recent NSR
Improvement rule promulgated in December 2002, and the comments we
received on the proposed revisions to part 70 and draft White Paper
Number 3, we propose revising the part 70 and 71 regulations and part
51 and 52 regulations.
As explained further below, the proposed revisions to the operating
permit programs of parts 70 and 71 add a definition and clarify
requirements for ``alternative operating scenario'' (or ``AOS'') and
add a definition for ``approved replicable methodology'' (or ``ARM'').
The proposed revisions to the major NSR program add a definition and
codify requirements for Green Groups.
The primary purpose of these revisions to parts 70 and 71 is to
build upon the existing regulatory framework and ensure that the
flexible permitting approaches with which we have experience are more
readily and widely used. We recognize that many States' minor NSR and
part 70 programs may already provide for the flexible permitting
approaches proposed and that such States are currently able to
implement these approaches. Because of the diversity of existing State
minor NSR programs and our pilot experience indicating the ability of
many programs to approve categories of future changes in advance of
making those changes, we are not proposing any revisions to the rules
governing State minor NSR programs at 40 CFR 51.160 through 51.164. By
undertaking the part 70 rulemaking, it is not our intention to preclude
States from continuing to develop and use flexible permit approaches,
where their current regulatory structure provides authority to do so.
This rulemaking is instead intended to encourage the use of advance
approvals where available and appropriate, and to eliminate any
uncertainty that may exist with respect to AOSs and to provide a clear
regulatory pathway governing flexible air permit development in that
area by clarifying our 1992 part 70 regulations.\11\
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\11\ Note that other approaches to AOSs and advance approval may
also be acceptable, although they may not provide as much
flexibility as the approaches proposed. For example, some States
include in a title V permit a type of conditional approval under
which a source cannot construct or operate otherwise approved
changes until a minor NSR approval is obtained for them.
Essentially, this approach creates in a title V permit a structure
that is a precursor to an AOS or an advance approval. Once the minor
NSR permit is issued, the source can construct and operate the
changes under the conditional approval, but a title V permit
revision is needed to incorporate the now-available minor NSR terms
and to award the permit shield (where available from the permitting
authority). Where an AOS is involved, this incorporation is also
needed to complete the AOS consistent with 40 CFR 70.6(a)(9). Our
pilot permit experience suggests that in many instances changes
subject to minor NSR can be approved in advance, although the
ability for a State to provide such approvals will vary depending on
the actual provisions of individual State rules. As a result, where
advance approval of changes subject to minor NSR is available, we
encourage its incorporation into the title V permit after or
concurrent with obtaining the necessary minor NSR approvals in order
to provide a permitting strategy with greater operational
flexibility, certainty, and permitting efficiency than does a
conditional approval approach.
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The proposed revisions to parts 51 and 52 affecting major NSR
programs will increase options for flexible permits under that program.
Namely, the proposed provisions for Green Groups will offer operational
flexibility options for a defined section of a plant. This option would
augment the plantwide strategy previously promulgated in the NSR
Improvement rule (i.e., PALs). The proposed revisions would modify the
major NSR regulations in a limited way. Consistent with the current NSR
requirements, we propose to clarify that the definition of emissions
unit would allow a number of emission activities, meeting certain
criteria, to be treated as a single emissions unit (i.e., a ``Green
Group''). We are proposing to change the current NSR requirements to
provide expressly for Green Groups so as to authorize in a major NSR
permit that emissions increases and changes within such a group can
occur over a 10-year period, provided the increases and changes are
authorized in advance through major NSR and the emissions activities
associated with the Green Group are controlled to the level determined
to be BACT/LAER. Also, the requirements of 40 CFR 52.21(j)(4) and
51.166(j)(4) requiring reevaluation of BACT for phased construction
projects and of 40 CFR 52.21(r)(2) requiring continuous construction to
commence within 18 months would not apply to NSR permits involving
Green Groups.
We believe that these proposed revisions will increase operational
flexibility, while ensuring environmental protection and compliance
with applicable requirements. Moreover, based on our pilot experience,
we anticipate that these revisions will promote improved environmental
performance, although we recognize that the nature of the improvements
will depend on the numbers and types of sources that opt to use the
flexible permitting approaches described in this document.
IV. What experience did we gain from the 14-year pilot permit program?
This section summarizes the benefits of the pilot permits; includes
an overview of the sources', permitting authorities', and our
conclusions concerning the effectiveness of the pilot permits; and
presents our recommendations regarding public participation in flexible
permitting. Through the pilot permit program,\12\ which began in 1993,
we sponsored various projects, including projects undertaken through
the Agency's ``Pollution Prevention in Permitting Program'' (P4). The
pilot program generally involved the issuance of flexible air permits
designed to accommodate operational flexibility.
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\12\ Sources at the following locations participated in our
pilot permit program: (1) 3M (St. Paul, MN); (2) Intel (Aloha, OR);
(3) Lasco Bathware (Yelm, WA); (4) Imation (Weatherford, OK); (5)
Cytec (Connecticut); (6) DaimlerChrysler (Newark, DE); (7) Merck
(Elkton, VA); (8) Merck (Barceloneta, PR); (9) Saturn (Spring Hill,
TN); (10) BMW (Spartanburg, SC); (11) Eli Lilly (West Lafayette,
IN); (12) 3M (Nevada, MO); and (13) Imation (Camarillo, CA).
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The pilot permits facilitated operational flexibility by first
obtaining advance approval under NSR. Frequently the authorizations
involved changes that were to occur under a PAL or other facility-wide
cap on emissions which, once approved by the relevant permitting
authority, served both to assure that major NSR would not be
[[Page 52212]]
applicable to changes occurring under the cap and to assure that
ambient standards would be protected consistent with the requirements
of minor NSR.\13\ These caps were then incorporated into the title V
permit with appropriate permit terms and conditions. In most cases,
once these caps were incorporated into a title V permit, sources did
not need to seek additional approvals from the title V permitting
authority prior to implementing the changes authorized under the caps.
As necessary, the title V permit would also contain additional terms
and conditions needed to assure compliance with any other applicable
requirements applying to such changes.
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\13\ The VOC emissions caps used in the pilots were determined
to be adequate for purposes of safeguarding the ozone NAAQS, but for
other pollutants (e.g., air toxics) States sometimes required a
replicable modeling procedure to screen the impacts of individual
emissions increases relative to acceptable ambient toxics levels.
Here an ambient dispersion model, complete with implementation
assumptions, is approved into the minor NSR permit to evaluate any
new pollutant of concern or increased existing pollutant emissions.
Failure of a particular change to meet the screening levels
triggered the need for case-by-case review of that change from the
permitting authority.
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As noted above, following issuance of the pilot permits, we
conducted an in-depth review of six of the permits.\14\ In selecting
the permits to review, we focused our evaluation on those pilots with
sufficient implementation experience to provide a reasonable historical
record of performance, and we continue to believe that these pilots
represent a sufficiently diverse reference point from which to judge
the effectiveness of flexible air permits over a broad range of
sources. Those reviews involved: (1) Detailed analyses of the sources'
and permitting authorities' experiences developing and implementing the
pilot permits; (2) a thorough review of information available in the
public record at the permitting authority; (3) discussions with source
personnel; (4) site visits to the source and meetings with permitting
authorities; and (5) independent verification of compliance status and
data collection and management techniques, including recordkeeping and
related requirements.
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\14\ The six permits that we analyzed were: (1) Intel (Aloha,
OR); (2) 3M (St. Paul, MN); (3) Lasco Bathware (Yelm, WA); (4)
DaimlerChrysler (Newark, DE); (5) Saturn (Spring Hill, TN); and (6)
Imation (Weatherford, OK).
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Our analyses revealed several benefits of the flexible permitting
approaches used in the pilots, and those benefits are summarized
briefly below. We invite comment on any similar or different
experiences others have had in piloting flexible air permits,
particularly where these experiences are relevant to this rulemaking.
A. What were the benefits of the pilot permits?
This section provides an overview of the environmental,
informational, economic, and administrative benefits of the flexible
pilot permits. For additional information on these and other benefits
of the pilot program, please refer to the ``Evaluation of the
Implementation Experience with Innovative Air Permits,'' which
documents all of our findings concerning the six pilot permits that we
evaluated.\15\
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\15\ Among other things, the report confirmed that the flexible
permits are enforceable in a practical manner by EPA and permitting
authorities. See Report at pages 5, 20. See footnote 9 of this
preamble for information on how you can obtain the report.
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1. Environmental Improvements Achieved Using Flexible Permits
In our evaluation, we documented several environmental performance
benefits of the flexible pilot permits, including that the permits
facilitated emissions reductions and increased P2 efforts. In
particular, as discussed further below, the emissions cap framework in
the flexible permits enabled significant reductions in actual plantwide
emissions and/or emissions per unit of production. For example, of the
five sources that had operated under their flexible permits for 3 or
more years, all five achieved 30-to 80-percent reductions in actual
plantwide emissions and/or emissions per unit of production. Actual
emissions from the sixth source were reduced by 27 percent in the first
year of operation under its flexible permit, but it is difficult to
draw conclusions based on a single year of data. One company, using P2,
lowered its actual volatile organic compound (VOC) emissions by 70%
(from 190 tons per year (tpy) to 56 tpy), while increasing production.
This allowed the facility to commit to keeping its VOC emissions below
the major source threshold (i.e., become a ``synthetic minor'' source)
so that it was no longer subject to major NSR. Another company lowered
its actual VOC emissions from 1,400 tpy to less than 800 tpy, primarily
through P2 associated with vehicle coatings and plant solvent usage.
We attribute the environmental performance improvement benefits of
the flexible permits to several factors. First, several companies
reported that the emissions caps had a ``focusing effect,'' drawing
company personnel(s attention on how to manage most effectively all of
the activities within the plant, even those not subject to regulation,
in an effort to minimize total plantwide emissions.\16\ An emissions
cap also creates incentives for companies to pursue additional
emissions reduction opportunities to increase the margin of compliance,
which is the difference between the level of the emissions cap and the
source's actual total plantwide emissions. Larger compliance margins
typically reduce the risk of noncompliance with an emissions cap and
create room under the cap to accommodate future emissions increases
related to production or other operational changes. The cap on
emissions from the plant, which is set during permitting at a level
judged to be environmentally protective, ensures that such future
emissions increases together with existing emissions will not exceed
this protective level. To obtain a sufficient margin of compliance with
these caps, sources frequently voluntarily controlled emissions on
grandfathered units, which are units that would otherwise not be
subject to control, and increased the stringency of control on
regulated units.
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\16\ See the pilot permit report, ``Evaluation of the
Implementation Experience with Innovative Air Permits,'' page 22.
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Additionally, we found that the use of advance approvals and AOSs
improved operational efficiency at the plants because companies knew in
advance what changes were authorized, making resource allocation more
efficient and accommodating the typically incremental, iterative nature
of industrial process improvements. We also found that P2-related
projects became more attractive to the companies when advance approved
because such projects could be undertaken without the delay and
uncertainty of future case-by-case approvals. In addition, P2-related
projects reduced emissions and enabled sources to comply more easily
with emissions limits such as plantwide emissions caps.
2. Informational Benefits Achieved Using Flexible Permits
We have consistently maintained that including advance approvals
and AOSs in a title V permit ensures that the permit presents a
complete representation of the operations of the permitted facility.
See 57 FR 32276; July 21, 1992. By requiring information concerning
flexible permits as part of the permit application, EPA and the
permitting authorities are better able to assess, in aggregate, all
proposed operations and, more significantly, to
[[Page 52213]]
determine all relevant applicable requirements and to include in the
draft permit terms and conditions for each approved scenario to assure
compliance with those applicable requirements and the requirements of
part 70. By comparison, conventional permitting approaches provide for
a more narrow, case-by-case view of facility modifications, soliciting
comment only on the specific change proposed and requiring individual
permitting actions in response to each request by the permittee for a
change in the permit.
Our pilot experience confirmed the significant value of presenting
a comprehensive picture of a source(s operations over the term of the
title V permit. Specifically, we found that with proposed flexible
permits involving changes under a PAL or other emissions cap,
permitting authorities were better able to understand the scope of
planned changes at the source and the maximum, cumulative environmental
effects of those changes. In addition, the flexible permit applications
provided increased information to permitting authorities and the public
in areas such as plantwide emissions performance and P2 activities, as
compared to information typically available under conventional permit
approaches. Likewise, permitting authorities indicated that on balance,
flexible air permits enhanced the availability of information to the
public during permit implementation.
Moreover, through the pilots, we found that early public outreach
and involvement can be very useful in situations where new permitting
techniques have not previously been used in a particular jurisdiction.
We encourage permitting authorities to consider early outreach and
public involvement when implementing such permitting techniques until
the techniques become more widely used and public familiarity with them
increases, recognizing that other factors (e.g., permit complexity)
should factor into the permitting authority(s consideration of
supplemental public outreach efforts.
Our evaluation of the six pilot permits also revealed the
importance of reporting related to plantwide applicability limits. The
type of reporting required in several of the flexible permits is now
codified in the PAL provisions of the December 2002 NSR Improvement
rule.
3. Economic Benefits Achieved Using Flexible Permits
Participating companies in the pilot program reported that a
flexible air permit significantly reduces the uncertainty and
transaction costs associated with the title V permitting process
because the source obtains approval of the changes it reasonably
anticipates implementing during the 5-year term of the permit at one
time. Based on our evaluation of the six pilot permits, we found that
the increased certainty and reduced transaction costs improved
participating companies' ability to compete effectively in the market
and enabled them to retain, and in some cases, create jobs. For
example, one company reported that its pilot permit allowed it to
remain highly responsive to the marketplace and thereby avoid either
lost sales and/or permanent loss of market share. An automotive company
indicated that its flexible permit was a principal factor in the
plant's selection to manufacture an engine model to be used in the
company's global vehicle assembly operations, leading to the creation
of 700 jobs. The permit helped the plant secure the engine contract
because it enabled the plant to reduce the project time line for
production of the new engine to 24 months and to accommodate future
changes with minimal delay.\17\
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\17\ See ``EPA Flexible Permit Implementation Review: Saturn
Permit Review Report,'' pages 9 and 34, which is available at http:/
/www.epa.gov/ttn/oarpg/t5/memoranda/iap_sprr.pdf.
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Several companies also indicated that obtaining authorization of
reasonably anticipated changes improved the predictability of change
implementation time frames for project planning and avoided what can be
substantial opportunity costs. For example, one company reported that
its flexible permit likely saved hundreds of business days associated
with making operation and process changes to ramp up production for new
products, respond to market demands, and optimize production processes.
Industry estimates of the opportunity costs of production downtime and
time delays run as high as millions of dollars in just a few days due
to lost sales and other factors.\18\
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\18\ Findings are discussed in more detail in the ``Evaluation
of Implementation Experiences with Innovative Air Permits'' report,
under Finding 8.
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Notwithstanding that the implementation of flexible air permits
often was associated with more production-related jobs, pilot companies
also reported that flexible air permits significantly reduced permit-
related staff time and related resource costs because there was no
longer a need to seek and process multiple case-by-case permit actions
because the changes reasonably anticipated at the facility were already
included and approved in the permit. For example, an automotive company
estimated that it saved approximately 505 hours of staff time during
its initial flexible permit term. Another pilot company reported
permit-related staff time savings of 1,200 to 1,600 hours per year
during its initial title V permit term. In both cases, companies
reported that the time savings enabled environmental personnel to focus
more time and attention to other environmental management activities,
including P2. Companies further indicated that the time necessary to
record changes in operating scenarios in the on-site log, as required
by 40 CFR 70.6(a)(9), was significantly less than the permit-related
staff time necessary to prepare permit applications under a general
change-by-change permitting approach.
4. Administrative Benefits Achieved Using Flexible Permits
Our pilots evaluation found that the flexible permits resulted in a
net cost savings both for the source, as noted above, and for the
permitting authority. We specifically found that the resources
permitting au