Prevention of Significant Deterioration for Nitrogen Oxides, 8880-8917 [05-3366]
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8880
Federal Register / Vol. 70, No. 35 / Wednesday, February 23, 2005 / Proposed Rules
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 51 and 52
[AD–FRL–7875–1; E–Docket ID No. OAR–
2004–0013 (Legacy Docket No. A–87–16)]
RIN–2060–AM33
Prevention of Significant Deterioration
for Nitrogen Oxides
AGENCY: Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
SUMMARY: To preserve the air quality in
national parks and other areas that are
meeting the national ambient air quality
standards (NAAQS) for nitrogen dioxide
(NO2), EPA is reevaluating the
increments for NO2 that were first
established in 1988 under its program to
prevent significant deterioration of air
quality (PSD program). The EPA is
initiating this rulemaking action to
comply with a 1990 court ruling that
directed the Agency to consider and
harmonize the statutory criteria for
establishing PSD regulations for
nitrogen oxides (NOX) contained in
sections 166(c) and 166(d) of the Clean
Air Act (CAA or Act).
After an initial reevaluation of the
existing NO2 increments under these
statutory criteria, EPA is proposing
three options. One proposed option is
not to change the existing increments.
We are also proposing two other options
that would allow States to use
alternative approaches in lieu of the
existing increments for NO2 to satisfy
the statutory criteria for preventing
significant deterioration of air quality
due to emissions of NOX. These
proposed options include
implementation of either an EPAadministered cap and trade program or
a State planning approach.
DATES: Comments. Comments must be
received on or before April 25, 2005.
Public Hearing. If anyone contacts
EPA requesting a public hearing by
March 15, 2005, we will hold a public
hearing on or about March 25, 2005.
ADDRESSES: Submit your comments,
identified by Docket ID No. OAR–2004–
0013, by one of the following methods:
• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the on-line
instructions for submitting comments.
• Agency Web site: https://
www.epa.gov/edocket. EDOCKET, EPA’s
electronic public docket and comment
system, is EPA’s preferred method for
receiving comments. Follow the on-line
instructions for submitting comments.
• E-mail: a-and-rdocket@email.epa.gov.
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• Fax: (202) 566–1741.
• Mail: Attention Docket ID No.
OAR–2004–0013, U.S. Environmental
Protection Agency, Mailcode 6102T,
1200 Pennsylvania Ave., NW.,
Washington, DC 20460. The EPA
requests that a separate copy also be
sent to the contact person listed below
(see FOR FURTHER INFORMATION CONTACT).
• Hand Delivery: Attention Docket
Number OAR–2004–0013, U.S.
Environmental Protection Agency, EPA
West (Air Docket), 1301 Constitution
Ave., NW., Washington, DC 20004. Such
deliveries are only accepted during the
Docket’s normal hours of operation, and
special arrangements should be made
for deliveries of boxed information. The
EPA requests a separate copy also be
sent to the contact person listed below
(see FOR FURTHER INFORMATION CONTACT).
Instructions: Direct your comments to
Docket ID No. OAR–2004–0013 (Legacy
Docket No. A–87–16). The EPA’s policy
is that all comments received will be
included in the public docket without
change and may be made available
online at https://www.epa.gov/edocket,
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
EDOCKET, regulations.gov, or e-mail.
The EPA EDOCKET and the Federal
regulations.gov Web sites are
‘‘anonymous access’’ systems, 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
EDOCKET or 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, avoid any
form of encryption, and be free of any
defects or viruses. For additional
information about EPA’s public docket,
visit EDOCKET on-line or see the
Federal Register of May 31, 2002 (67 FR
38102). For additional instructions on
submitting comments, go to section I.B
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of the SUPPLEMENTARY INFORMATION
section of this document.
Docket: All documents in the docket
are listed in the EDOCKET index at
https://www.epa.gov/edocket. 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 EDOCKET or in hard
copy at the U.S. Environmental
Protection Agency, EPA West (Air
Docket), Room B102, 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 for
the Air Docket is (202) 566–1742.
Public Hearing. People interested in
presenting oral testimony or inquiring
as to whether a hearing is to be held
should contact Ms. Chandra Kennedy,
OAQPS, Integrated Implementation
Group, Information Transfer and
Program Integration Division (C339–03),
U.S. Environmental Protection Agency,
Research Triangle Park, NC 27711,
telephone number (919) 541–5319 or email kennedy.chandra@epa.gov, at least
2 days in advance of the public hearing.
People interested in attending the
public hearing must also call Ms.
Kennedy 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 the proposed
action. If a public hearing is held, it will
be held at 10 a.m. in EPA’s Auditorium
in Research Triangle Park, North
Carolina, or at an alternate site nearby.
FOR FURTHER INFORMATION CONTACT: Mr.
Dan deRoeck, Information Transfer and
Program Integration Division (C339–03),
U.S. Environmental Protection Agency,
Research Triangle Park, NC 27711,
telephone (919) 541–5593, fax (919)
541–5509, or e-mail at
deroeck.dan@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Action Apply to Me?
Entities potentially affected by this
proposed rule include sources in all
industry groups. The majority of sources
potentially affected are expected to be in
the following groups:
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SIC a
Industry group
Electric Services ...........................................................................................................................................
491
Petroleum Refining .......................................................................................................................................
Industrial Inorganic Chemicals .....................................................................................................................
291
281
Industrial Organic Chemicals .......................................................................................................................
286
Miscellaneous Chemical Products ...............................................................................................................
289
Natural Gas Liquids ......................................................................................................................................
Natural Gas Transport ..................................................................................................................................
Pulp and Paper Mills ....................................................................................................................................
132
492
261
Paper Mills ....................................................................................................................................................
Automobile Manufacturing ............................................................................................................................
262
371
Pharmaceuticals ...........................................................................................................................................
283
8881
NAICS b
221111, 221112, 221113,
221119, 221121, 221122
324110
325181, 325120, 325131,
325182, 211112, 325998,
331311, 325188
325110, 325132, 325192,
325188, 325193, 325120,
325199
325520, 325920, 325910,
325182, 325510
211112
486210, 221210
322110, 322121, 322122,
322130
322121, 322122
336111, 336112, 336211,
336992, 336322, 336312,
336330, 336340, 336350,
336399, 336212, 336213
325411, 325412, 325413,
325414
a Standard
b North
Industrial Classification
American Industry Classification System.
Entities potentially affected by the
proposal also include States, local
permitting authorities, and Indian
Tribes whose lands contain new and
modified major stationary sources.
B. What Should I Consider as I Prepare
My Comments for EPA?
1. Submitting CBI
Do not submit proprietary or
confidential business information (CBI)
to EPA through EDOCKET,
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. Send an additional copy,
clearly marked as CBI, as above, to: Mr.
Roberto Morales, OAQPS Document
Control Officer (C339–03), U.S.
Environmental Protection Agency,
Research Triangle Park, NC 27711.
2. Tips for Preparing Your Comments
When submitting comments,
remember to:
i. Identify the rulemaking by docket
number and other identifying
information (e.g., subject heading,
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date and reference page number(s)).
ii. 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.
iii. Explain why you agree or disagree;
suggest alternatives and provide
substitute language for your requested
changes.
iv. Describe any assumptions and
provide any technical information and/
or data that you used.
v. If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
vi. Provide specific examples to
illustrate your concerns, and suggest
alternatives.
vii. Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
viii. Make sure to submit your
comments by the comment period
deadline identified.
C. Where Can I Obtain Additional
Information?
In addition to being available in the
docket, an electronic copy of today’s
proposed rule is also available on the
World Wide Web through the
Technology Transfer Network (TTN).
Following signature by the EPA
Administrator, a copy of today’s
proposed rule will be posted on the
TTN’s policy and guidance page for
newly proposed or promulgated rules at
https://www.epa.gov/ttn/oarpg. The TTN
provides information and technology
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exchange in various areas of air
pollution control. If more information
regarding the TTN is needed, call the
TTN HELP line at (919) 541–5384.
D. How Is this Preamble Organized?
The information presented in this
preamble is organized as follows:
I. General Information
A. Does This Action Apply To Me?
B. What Should I Consider as I Prepare My
Comments for EPA?
C. Where Can I Obtain Additional
Information?
D. How Is This Preamble Organized?
II. Overview of Today’s Proposed Action
A. Option 1: Retain Existing Increment
System for NOX
B. Option 2: Allow States To Use a Cap and
Trade Program in Lieu of an Increment
System for NOX
C. Option 3: Allow States Flexibility To
Use a State Planning Approach in Lieu
of an Increment System for NOX
III. Background
A. PSD Program
B. Existing Section 166 Regulations for
NOX
1. Statutory Provisions
2. The 1988 NO2 Increments
C. Court Decision
IV. Legal Authority
A. Interpretation on Remand: Harmonizing
Sections 166(c) and 166(d) of the Clean
Air Act
B. Interpretation on Remand: The Section
166(c) Factors
1. Numerical Measures by Which Permit
Application May Be Evaluated
2. Protect Air Quality Values
3. Protect Public Health and Welfare From
Adverse Effects Notwithstanding
Attainment of NAAQS
4. Ensure Economic Growth Consistent
With Preservation of Existing Clean Air
Resources
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C. EPA’s Authority To Fulfill Section 166
Requirements by Granting States
Flexibility To Adopt Alternative
Measures in Their SIPs
V. Health and Welfare Effects of NOX
A. Scope of Effects EPA Proposes To
Consider
B. Data Included in Review
C. Analysis of Effects
1. Health Effects
2. Welfare Effects
VI. Proposed Actions
A. Retain Existing Increment System for
NOX
1. How Existing Characteristics of the
Regulatory Scheme Fulfill Statutory
Criteria
2. Proposed Actions Regarding
Characteristics of NO2 Increments
B. Regional Cap and Trade Program
1. Description of Cap and Trade Programs
2. Using a Cap and Trade Program in Lieu
of an Increment System for NOX
C. State Planning Approach
1. Description of State Planning Approach
2. Using State Planning Approach in Lieu
of an Increment System for NOX
VII. Other Alternative Considered
VIII. 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. Overview of Today’s Proposed
Action
To ensure protection of the air quality
in national parks and other areas that
meet the NAAQS for NO2, EPA is
reevaluating the NO2 increments that
were first established in 1988 under the
PSD program. In accordance with the
directions of a 1990 court ruling, the
Agency is conducting this review to
consider and harmonize the statutory
criteria, contained in subsections 166(c)
and 166(d) of the Act, that govern the
content of EPA’s pollutant-specific PSD
regulations for NOX. The EPA is
proposing to apply these criteria using
the ‘‘contingent safe harbor’’ approach
that was suggested by the court as an
appropriate way to ensure that EPA’s
PSD regulations for nitrogen oxides will
prevent significant deterioration of air
quality due to emissions of NOX in
parks and other areas that are either
designated to be in attainment with the
NAAQS or are unclassifiable.
Today’s proposal includes three
options to address our responsibility to
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promulgate pollutant-specific
regulations to prevent significant
deterioration of air quality from
emissions of NOX and to preserve,
protect and enhance the air quality in
our national parks and other areas of
special interest. The first option is to
retain the existing regulatory format
using the increments that we originally
adopted in 1988. We also propose two
alternative approaches that we believe
would satisfy the goals and objectives of
the statutory PSD program in lieu of the
existing NO2 increments. These two
additional options, for which we are
seeking public comment today, would
permit States to adopt a specific marketbased cap and trade approach or to
demonstrate that strategies and
measures in their State Implementation
Plans (SIPs), in conjunction with other
Federal requirements, will prevent
significant deterioration of air quality
due to emissions of NOX. Each of these
options is summarized immediately
below and described in greater detail in
section VI of this preamble.
A. Option 1: Retain Existing Increment
System for NOX
The EPA is reviewing whether,
considering the criteria in section
166(c), EPA should establish different
increments for NOX than the ones that
were adopted in 1988. The existing
increments were established as a
percentage of the NAAQS, and were
based on the ambient measure (NO2)
and the same time period (annual) as
the NAAQS. An increment with these
characteristics satisfies the minimum
requirements of section 166(d) of the
Act for preserving the air quality in
parks and other attainment and
unclassifiable areas. In accordance with
the ‘‘contingent safe harbor’’ approach,
EPA is undertaking this additional
review to determine whether the criteria
in section 166(c) indicate that it is
necessary for EPA to deviate from this
‘‘safe harbor’’ in order to satisfy the
criteria in section 166(c).
Based on our initial review of the
existing NO2 increments under these
statutory criteria, one option is to retain
the existing PSD regulations for NOX,
which includes the existing NO2
increments, without modification
because we believe the existing
regulations protect the air quality in
national parks and other attainment or
unclassifiable areas, within the context
of the criteria of section 166(c). Our
review has considered and balanced the
criteria in section 166(c) and the
incorporated goals and purposes of the
PSD program set forth in section 160 of
the Act. We have also reviewed the
existing regulatory framework of the
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Agency’s PSD regulations for NOX and
the scientific and technical information
pertaining to the health, welfare, and
ecological effects of NOX. In light of this
review, EPA believes that the statutory
requirements are met by retaining
annual NO2 increments based on the
percentages of the NAAQS employed to
set the increments for sulfur dioxide
(SO2). The available research on health
and welfare effects indicates that the
existing increments, in conjunction with
the case-by-case permit review for
additional impacts and impairment of
air quality related values (AQRV),
fulfills the criteria in section 166(c). The
EPA requests comment on this option
and its supporting review.
B. Option 2: Allow States To Use a Cap
and Trade Program in Lieu of an
Increment System for NOX
As an alternative approach to
retaining the existing increment system
for NOX, we are soliciting comments on
a proposed option that would allow
States to prevent significant
deterioration of air quality due to
emissions of NOX by implementing the
model cap and trade program for EGUs
contained in our proposed Clean Air
Interstate Rule (CAIR).1 A State that
implements this program to address
NOX emissions would no longer be
required to conduct certain sourcespecific analyses, including the current
NO2 increment analysis.
This option would require States to
revise their SIPs to include a cap and
trade program to reduce NOX emissions
in accordance with statewide emissions
budgets prescribed by EPA. Neither the
statewide budget nor the regional cap
would be a legally enforceable limit on
total NOX emissions but would be used
as an accounting technique to determine
the amount of emissions reductions that
would be needed from specific source
categories to satisfy the budget or cap.
The requirements of the cap and trade
program would be enforceable, and this
would ensure that as long as emissions
from sources outside of the cap did not
grow more than projected, the overall
regionwide budget would be met.
As described in greater detail in
section VI.B of this preamble, we
believe that such a cap and trade
program, while designed to address
other CAA program requirements, is
also an effective alternative to
1 EPA proposed the CAIR, originally called the
Interstate Air Quality Rule (IAQR), on January 30,
2004 (69 FR 4566), followed by a supplemental
notice of proposed rulemaking on June 10, 2004 (69
FR 32684), to reduce emissions of SO2 and NOX in
29 States and the District of Columbia to contribute
to the attainment of the PM2.5 and 8-hour ozone
NAAQS in a number of eastern States.
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increments for preventing significant
deterioration from emissions of NOX.
The EPA has utilized this approach with
considerable success in several
instances. The EPA proposed a model
multi-State cap and trade program in its
June 10, 2004, supplemental notice for
the CAIR proposal that States could
choose to adopt to meet the proposed
emissions reductions requirements in a
flexible and cost-effective manner. The
EPA believes that the implementation of
this kind of cap and trade program
could bring about significant
improvements in air quality and would
offer many advantages over traditional
command-and-control and project-byproject emissions reduction credit
trading programs.
C. Option 3: Allow States Flexibility To
Use a State Planning Approach in Lieu
of an Increment System for NOX
As a third option, we propose to allow
a State to forego implementation of the
NO2 increments and associated
requirements if the State can
demonstrate that measures in its SIP, in
conjunction with Federal requirements,
would prevent significant deterioration
of air quality from emissions of NOX. In
lieu of implementing the increment
system for NOX, a State would have to
demonstrate that the specific planning
goals and requirements contained in its
SIP would satisfy the requirements in
section 166 of the Act and the goals and
purposes of the PSD program set forth
in section 160.
This option would provide States
with the flexibility to design a program
to prevent significant deterioration of air
quality from emissions of NOX that may
be more effective than increments.
States would have to establish a clear
planning goal that satisfies the
requirements of sections 166(c) and
166(d) of the Act. To achieve this goal,
a State could impose NOX emissions
limitations on any type of emissions
sources it chooses, including new or
existing sources. Under this option, EPA
does not propose to require a State to
demonstrate that its SIP includes a
specific type of program that we believe
is sufficient to satisfy the requirements
of section 166. However, we believe that
a goal to keep statewide emissions of
NOX from all sources below 1990 levels
would prevent significant deterioration
of air quality and satisfy the
requirements of section 166 of the Act.
Adoption of this goal could streamline
our review of the State’s demonstration,
but a State would not be precluded from
using another approach to prevent
significant deterioration of air quality
due to emissions of NOX.
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III. Background
A. PSD Program
Part C of title I of the Act contains the
requirements for a component of the
major new source review (NSR) program
known as the Prevention of Significant
Deterioration (PSD) program. This
program sets forth procedures for the
preconstruction review and permitting
of new and modified major stationary
sources of air pollution locating in areas
meeting the NAAQS (‘‘attainment’’
areas) or areas for which there is
insufficient information to classify an
area as either attainment or
nonattainment (‘‘unclassifiable’’ areas).
The applicability of the PSD program
to a particular source must be
determined in advance of construction
and is pollutant specific. For new
sources locating in an attainment or
unclassifiable area, PSD applies when
the source qualifies as a major source
because it has the potential to emit any
regulated NSR pollutant equals or
exceeds either 100 or 250 tons per year
(tpy) depending on the source category.
In addition to reviewing the pollutant
emitted at or in excess of the ‘‘major
source’’ levels, the PSD permit review
also covers each regulated NSR
pollutant for which the area is in
attainment or unclassifiable that the
source would have the potential to emit
in significant amounts.
For modified sources, PSD applies
when an existing major stationary
source undergoes a nonexcluded
physical change or change in the
method of operation that results in a
significant net emissions increase of any
regulated NSR pollutant for which the
area is in attainment or unclassifiable.
The PSD regulations define
‘‘significant’’ as a specific emissions rate
(tons per year) for each regulated
pollutant. Each regulated NSR pollutant
emitted by the source must be reviewed
independently for applicability
purposes. Moreover, to determine the
emissions of a particular pollutant for
applicability purposes, the source may
take into account the use of emissions
control technology and restrictions on
the hours of operation or rates of
production, where such controls and
restrictions are enforceable.2
2 On December 31, 2002, we revised the PSD
regulations to, among other things, enable major
sources undergoing modification of existing
emissions units to project future emissions
increases on the basis of projected utilization of the
modified equipment. Most States have not yet
adopted the new provisions but they are in effect
in States where EPA is the permitting authority (i.e.,
where no State PSD rule has been approved by
EPA) or where the State PSD rule incorporates the
Federal regulations by reference. 67 FR 80186; 68
FR 11316 (March 10, 2003).
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Once a source is determined to be
subject to PSD, it must undertake a
series of analyses to demonstrate that it
will use the best available control
technology (BACT) and will not cause
or contribute to a violation of any
NAAQS or incremental ambient
pollutant concentration increase. In
cases where the source’s emissions may
adversely affect an area classified as a
Class I area, additional review is
conducted to protect the increments and
special attributes of such an area
defined as ‘‘air quality related values.’’
When the permitting authority
reaches a preliminary decision to
authorize construction of each proposed
major new source or major modification,
it must provide notice of the
preliminary decision and an
opportunity for comment by the general
public, industry, and other persons that
may be affected by the major source or
major modification. After considering
and responding to the comments, the
permitting authority may issue a final
determination on the construction
permit in accordance with the PSD
regulations.
B. Existing Section 166 Regulations for
NOX
1. Statutory Provisions
In section 166(a) of the Act, Congress
directed EPA to conduct a study and
promulgate regulations to prevent
significant deterioration of air quality
which would result from emission of
hydrocarbons, carbon monoxide,
photochemical oxidants, and NOX.
Congress further specified that such
regulations meet the following
requirements set forth in sections 166(c)
and 166(d):
(c) Such regulations shall provide specific
numerical measures against which permit
applications may be evaluated, a framework
for stimulating improved control technology,
protection of air quality values, and fulfill the
goals and purposes set forth in section 101
and section 160.
(d) The regulations * * * shall provide
specific measures at least as effective as the
increments established in section 163 [for
SO2 and PM] to fulfill such goals and
purposes, and may contain air quality
increments, emission density requirements,
or other measures.
The goals and purposes of the PSD
program set forth in section 160 are as
follows:
(1) to protect public health and welfare
from any actual or potential adverse effect
which in the Administrator’s judgment may
reasonably be anticipate[d] to occur from air
pollution or from exposures to pollutants in
other media, which pollutants originate as
emissions to the ambient air,
notwithstanding attainment and maintenance
of all national ambient air quality standards;
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(2) to preserve, protect, and enhance the air
quality in national parks, national wilderness
areas, national monuments, national
seashores, and other areas of special national
or regional natural, recreational, scenic, or
historic value;
(3) to insure that economic growth will
occur in a manner consistent with the
preservation of existing clean air resources;
(4) to assure that emissions from any
source in any State will not interfere with
any portion of the applicable implementation
plan to prevent significant deterioration of air
quality for any other State; and
(5) to assure that any decision to permit
increased air pollution in any area to which
this section applies is made only after careful
evaluation of all the consequences of such a
decision and after adequate procedural
opportunities for informed public
participation in the decisionmaking process.
Furthermore, the goals and purposes
of the CAA set forth in section 101 are
as follows:
(b) * * * (1) to protect and enhance the
quality of the Nation’s air resources so as to
promote the public health and welfare and
the productive capacity of its population;
(2) to initiate and accelerate a national
research and development program to
achieve the prevention and control of air
pollution;
(3) to provide technical and financial
assistance to State and local governments in
connection with the development and
execution of their air pollution prevention
and control programs; and
(4) to encourage and assist the
development and operation of regional air
pollution prevention and control programs
[; and]
(c) * * * to encourage or otherwise
promote reasonable Federal, State, and local
governmental actions, consistent with the
provisions of this Act, for pollution
prevention.
2. The 1988 NO2 Increments
On October 17, 1988, EPA
promulgated pollutant-specific PSD
regulations for NOX under section 166
of the CAA. 53 FR 40656. The EPA
decided to establish NO2 increments
following the pattern enacted by
Congress for the PM and SO2
increments. These increments establish
maximum increases in ambient air
concentrations of NO2 (expressed in
micrograms per cubic meter (µg/m3))
allowed in a PSD area over a baseline
concentration. Emissions increases from
both stationary and mobile sources are
considered in the consumption of the
NO2 increments which are implemented
through the PSD permitting provisions
in 40 CFR parts 51 and 52.
The increment system for NOX
includes the three-tiered area
classification system established by
Congress in section 163 for increments
of SO2 and PM. Class I areas (including
certain national parks and wilderness
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areas) were designated by Congress as
areas of special national concern, where
the need to prevent air quality
deterioration is the greatest.
Consequently, the allowable level of
incremental change in air quality is
most stringent in Class I areas. Class II
areas are all areas not specifically
designated in the Act as Class I areas.
The increments of Class II areas are less
stringent than the Class I areas and
allow for a moderate degree of
emissions growth. Class III areas are
areas originally designated as Class II,
that have been redesignated by States
where higher levels of industrial
development (and emissions growth) are
desired, and are allowed to have the
greatest increase in ambient
concentration. There have been no Class
III redesignations to date.
EPA based the levels of the
increments for each area classification
on the percentages of the NAAQS that
Congress used to set the increments for
SO2 and PM. Congress used different
percentages of the NAAQS to calculate
the Class I increments for PM and SO2.
For the NO2 increments, we chose the
percentage that Congress used for SO2.
This decision yielded a lower Class I
increment for NO2 than would have
resulted by using the PM percentage.
The existing Class I NO2 increment is
2.5 µg/m3 (annual average), a level of 2.5
percent of the NO2 NAAQS. It is based
on the Class I SO2 increment, which is
set at the same percentage (2.5 percent)
of the SO2 annual NAAQS. The Class II
NO2 increment is 25 µg/m3·25 percent
of the NO2 NAAQS. The Class III NO2
increment is 50 µg/m3·50 percent of
the NO2 NAAQS.
EPA believed that these increments
satisfied the standard in section 166(d),
which requires that PSD regulations for
NOX be ‘‘at least as effective’’ as the
existing section 163 increments in
preventing significant deterioration of
air quality due to emissions of NOX. The
EPA thought that reflecting the same
percentages of the NAAQS as the SO2
and PM increments would be at least as
stringent as the statutorily established
increments in terms of ambient air
quality impacts. In the preamble to
these regulations, EPA explained that
the increments satisfied the section
166(c) criteria by providing numerical
measures against which permit
applications may be evaluated and
stimulating improved control
technology. The EPA relied on the
establishment of a Class I NO2
increment and the provisions for
protecting AQRVs in section 165(d)(2)
(providing a role for the Federal Land
Manager (FLM) in the review of certain
PSD permits prior to issuance) to protect
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air quality values affected by NOX. The
EPA further reasoned that these ambient
concentration percentages could be used
as a proxy for all the PSD purposes set
forth in the statute, thus satisfying the
‘‘goals and purposes set forth in section
101 and section 160’’ incorporated by
reference in section 166(c).
C. Court Decision
In 1988, the Environmental Defense
Fund (now Environmental Defense, or
‘‘ED’’) filed suit in the U.S. Court of
Appeals for the District of Columbia
Circuit against the Administrator
(Environmental Defense Fund, Inc. v.
Reilly, No. 88–1882). ED argued that
EPA failed to sufficiently consider
several of the section 166(c) criteria. ED
also argued that EPA’s approach failed
to satisfy the ‘‘at least as effective’’
standard under section 166(d) because
EPA did not compare the NO2
increments (set only for the annual
averaging period) to the 24-hour and 3hour increments for SO2.
In its 1990 opinion, the court held
that EPA had satisfied its obligation
under section 166(d) but had not
sufficiently considered whether
different increments should be
established under the criteria in section
166(c). More specifically, the court held
that EPA’s percentage-of-NAAQS
approach for determining the
increments satisfied the duty under
section 166(d) to promulgate regulations
for NOX that were ‘‘at least as effective’’
as the increments in section 163. Id. at
188. As to subsection (c), however, the
court held that EPA’s approach of using
the percentage ambient concentrations
as a ‘‘proxy’’ for meeting the subsection
(c) criteria overlooked the language of
subsection (c), and turned subsection (c)
into an option, despite its mandatory
wording. Thus, the court remanded the
case to EPA ‘‘to develop an
interpretation of section 166 that
considers both subsections (c) and (d),
and if necessary to take new evidence
and modify the regulations.’’
Environmental Defense Fund v. EPA,
898 F.2d 183, 190 (DC Cir. 1990) (‘‘EDF
v. EPA’’).
The court identified three steps that
EPA took to develop PSD regulations for
NOX under section 166. The first two
steps reflected EPA’s decisions to adopt
regulations for NOX that employed
increments with an area classification
system to implement the PSD program
for NOX. These first two steps were not
controverted in EDF v. EPA, 898 F.2d at
184–85. The dispute in the EDF case
involved only the third step, which was
EPA’s action to establish several
characteristics of the increments by
reference to the NAAQS. The
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characteristics that EPA derived from
the NAAQS were (1) the level of the
increments using the percent-ofNAAQS-approach; (2) the time period
(annual average) for the increments; and
(3) the pollutant (NO2) for which the
increments were established. Since
these three characteristics of the
increments were the only issues
controverted in the EDF v. EPA case,
EPA is revisiting only these questions to
satisfy the court’s remand. However, we
also believe it would be beneficial to
consider alternative approaches to an
increment system and thus are
voluntarily reconsidering the first two
steps in the process of developing
pollutant-specific PSD regulations for
NOX.
In EDF v. EPA, the court held that, in
light of the criteria in section 166(c),
EPA could not use the NAAQS as the
sole basis for deriving increments.
However, the court held that using the
NAAQS as the basis for deriving
increments was permissible in
determining whether the ‘‘at least as
effective’’ standard under subsection (d)
was met. But, with respect to subsection
(c), the court stated: ‘‘we find nothing in
the language or legislative history
suggesting that this duty [consideration
of the goals and purposes of the statute]
could be satisfied simply by referencing
the NAAQS.’’ Id. at 190. The court
noted the differences between the health
and welfare criteria on which the
NAAQS are based (sections 108 and
109) and the ‘‘goals and purposes’’ of
the PSD program set forth in section
160, highlighting the special value the
PSD program places on protection of
national parks. At the same time, the
court recognized that ‘‘[n]evertheless,
the ambient standards are the basic
measure of air quality under the [Clean
Air Act], and the controlling standards
by no means exclude any value that is
the subject of focus under the PSD
provisions.’’ Id. at 176 (internal citations
and quotations omitted). In other words,
the court observed that NAAQS remain
relevant to the inquiry under section
166 because they are a basic measure of
air quality and may indirectly reflect
some consideration, among others, of
the same values that are the focus of the
PSD program. However, the court
indicated that we could not rely solely
upon the NAAQS to comply with
section 166 because this provision
directs us to focus on the specific goals
and purposes of PSD which are not
necessarily the factors that determine
the NAAQS under section 109.
Thus, the court directed EPA to
reconsider the characteristics of the
existing increments in light of the
criteria in both sections 166(c) and
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166(d). The court indicated that one
permissible interpretation for
harmonizing subsections (c) and (d)
would be to construe subsection (d) as
a ‘‘contingent safe harbor’’ or
presumptive baseline. Thus, increments
derived from the NAAQS could be
authorized if the agency were to
undertake additional analysis and make
a reasoned determination that the
criteria under subsection (c) do not call
for different increments than the ‘‘safe
harbor’’ that meets the criteria in
subsection (d) of the statute.
On July 31, 2003, Environmental
Defense (ED) petitioned the court to
order EPA to take action in accordance
with the court’s earlier opinion. ED and
EPA reached a settlement in which EPA
agreed to propose and promulgate a rule
to fully comply with the court’s remand
order. The settlement obligated the
Agency to issue a proposal no later than
September 30, 2004, and a final rule no
later than September 30, 2005. However,
in September 2004, EPA and ED agreed
to extend the proposal deadline until
February 14, 2005 in order to allow EPA
more time to consider alternatives to the
increment approach.
IV. Legal Authority
Section 166(a) of the Act directs EPA
to develop pollutant-specific regulations
to prevent the significant deterioration
of air quality. Sections 166(c) and 166(d)
of the Act provide more detail on the
contents of those regulations. To
develop pollutant-specific regulations
under subsection (a), EPA must
establish an overall regulatory
framework for those regulations and fill
in many specific details around that
framework.
EPA interprets section 166 to require
that its PSD regulations for a particular
pollutant must, as a whole, satisfy the
criteria in section 166. Thus, we believe
our obligations under section 166(c) of
the Act are satisfied when the entire
body of pollutant-specific regulations
for NOX (including the overall
regulatory framework and the specific
details) satisfy the criteria in sections
166(c) and 166(d) of the Act.
In the case of NOX, EPA established
that overall framework in the 1988
rulemaking and employed NO2
increments and an area classification
system for these regulations.3 This
increment system for NOX was modeled
3 Under section 166(e) of the Act, a State is
authorized to develop measures to prevent
significant deterioration of air quality other than an
area classification scheme for pollutants other than
PM and SO2 if the implementation plan contains
other provisions that the Administrator finds will
‘‘carry out the purposes in section 160 at least as
effectively as an area classification plan for such
pollutant.’’
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on the system that Congress had already
established for PM and SO2. Within this
overall system, EPA then filled in
specific details, including defining the
characteristics of the increments to be
developed for NOX.
The dispute in EDF v. EPA involved
only EPA’s decisions to define the
characteristics of the increments for
NOX in relation to the NAAQS. Since
the basic increments and area
classification system in EPA’s PSD
regulations for NOX were not
controverted, EPA does not interpret the
court’s opinion to require that the
Agency reconsider these fundamental
aspects of its PSD regulations for NOX.
Thus, EPA believes that it is only
required at this time to reconsider the
level, time period, and pollutant used in
establishing increments in its PSD
regulations for NOX.
However, EPA is also requesting
comment in this proposed rule on
alternatives to the current increment
system for NOX. Based on the input
from various stakeholders, EPA is
voluntarily reconsidering whether the
increment system is the most effective
mechanism for fulfilling our obligations
to protect parks and other attainment
areas under section 166 of the Act.
Thus, as alternatives to our proposing to
retain the existing increment system for
NOX, we are also proposing to allow the
States to implement an EPAadministered cap and trade program or
a State planning approach to fulfill our
obligation to establish pollutant-specific
PSD regulations for NOX.
A. Interpretation on Remand:
Harmonizing Sections 166(c) and 166(d)
of the Clean Air Act
We propose to harmonize the criteria
set forth in sections 166(c) and 166(d)
by using the ‘‘contingent safe harbor’’
approach discussed by the Court. We
believe this is an appropriate reading of
the statute. Subsection (c) describes the
kinds of measures to be contained in the
regulations to prevent significant
deterioration of air quality called for in
section 166(a) and specifies that these
regulations are to ‘‘fulfill the goals and
purposes’’ set forth in sections 160 and
101 of the Act. Then, under subsection
(d), to ‘‘fulfill such goals and purposes,’’
EPA must promulgate ‘‘specific
measures at least as effective as the
increments established in section 7473
of this title [section 163 of the Act].’’ 42
U.S.C. 7476. Subsection (d) indicates
that these specific measures may
include increments but are not
necessarily required to contain
increments. Thus, subsection (d) can be
construed to require that EPA identify a
minimum level of effectiveness, or safe
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harbor, for the body of pollutant-specific
PSD regulations adopted under section
166. Then, subsection (c) may be read to
require that EPA conduct further review
to determine whether, based on the
criteria in subsection (c), EPA’s
pollutant-specific PSD regulations
under section 166 should contain
measures that deviate from the
minimum ‘‘safe harbor’’ identified
under subsection (d). As in 1988, we
construe subsection (d) to require that
the measures be ‘‘at least as stringent’’
as the statutory increments set forth in
section 163.
In an instance where EPA opts to
employ increments in its section 166
PSD regulations for a specific pollutant,
we interpret this language to require
that EPA, at minimum, establish
increments that are consistent with the
statutory increments established by
Congress in that each increment (Class
I, II, or III) is established in relation to
the NAAQS and is set (1) at an
equivalent percentage of the NAAQS as
the statutory increments; (2) for the
same pollutants as the NAAQS; and (3)
for the same time period as the NAAQS.
Under an increment approach, EPA
would then conduct further review to
determine whether the ‘‘safe harbor’’
increments, in conjunction with other
measures adopted under the PSD
program and section 166, sufficiently
fulfill the criteria in subsection (c). If,
after weighing and balancing the criteria
set forth in subsection (c) (and the
incorporated goals and purposes of the
CAA in section 101 and the PSD
program in section 160), EPA
determines that the ‘‘safe harbor’’
increments and other measures do not
satisfy these criteria, then EPA would
need to develop additional regulations
which may include different
increments, additional increments, or
additional measures to satisfy the
section 166(c) criteria. If EPA
determines that the ‘‘safe harbor’’
increments and associated measures
satisfy the criteria in subsection (c), then
it need not adopt different or additional
increments or other measures as part of
its PSD regulations under section 166.
B. Interpretation on Remand: The
Section 166(c) Factors
EPA interprets section 166(c) of the
Act to establish eight factors to be
considered in the development of PSD
regulations for the pollutants covered by
this provision. Section 166(c) lists three
specific criteria that EPA must consider
in the development of PSD regulations
for the pollutants covered by this
provision. These three criteria indicate
that PSD regulations for specific
pollutants should provide (1) specific
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numerical measures for evaluating
permit applications; (2) a framework for
stimulating improved control
technology; and (3) protection of air
quality values. 42 U.S.C. 7476(c). In
addition, section 166(c) directs that
EPA’s PSD regulations for specific
pollutants ‘‘fulfill the goals and
purposes’’ set forth in sections 101 and
160 of the Act. 42 U.S.C. 7476(c). We
interpret this phrase to incorporate the
five goals and purposes of the PSD
program set forth in section 160 as
factors that EPA must consider to
comply with section 166(c) of the Act.
The Agency’s view is that PSD
measures that satisfy the specific goals
and purposes of section 160 also satisfy
the more general purposes and goals
identified in section 101 of the Act. The
overall goals and purposes of the CAA
listed in sections 101(b) and 101(c) are
general goals regarding protecting and
enhancing the nation’s air resources and
controlling and preventing pollution.
Because these broad goals are given
more specific meaning in section 160,
EPA does not believe it is necessary to
consider them in detail when evaluating
whether PSD regulations satisfy the
criteria in section 166(c). In addition,
the court’s inquiry in EDF v. EPA
focused exclusively on the specific goals
and purposes of the PSD program set
forth in section 160. However, because
the broad purpose of the CAA set forth
in section 101(b)(1) provides some
additional guidance as to the meaning of
the more specific PSD goal set forth in
section 160(3), we discuss section
101(b)(1) further below in this limited
context of interpreting one of the factors
applicable under section 166.
Thus, EPA construes the term ‘‘fulfill
the goals and purposes,’’ as used in
section 166(c), to mean that EPA should
apply the goals and purposes listed in
section 160 as factors applicable to
pollutant-specific PSD regulations
established under section 166. The
EPA’s PSD regulations for NOX should
therefore be consistent with the three
criteria listed in section 166(c) and the
five goals and purposes listed in section
160 of the Act.
As noted above and explained further
below, for the increment option in this
proposal, we believe many of the eight
factors applicable under section 166(c)
are fulfilled by elements of the
regulatory framework that were
established in 1988 and not
controverted in EDF v. EPA. We discuss
further below how the proposed cap and
trade and State planning options also
satisfy these factors. The following
sections provide more detail on how we
propose to interpret and apply several of
these factors in developing pollutant-
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specific PSD regulations under section
166 of the Act.
1. Numerical Measures by Which Permit
Application May Be Evaluated
The first criterion in section 166(c)
states that pollutant-specific PSD
regulations must contain ‘‘specific
numerical measures against which
permit applications may be evaluated.’’
We believe an increment would clearly
satisfy this criterion but do not interpret
section 166 to require that we employ
an increment system for every pollutant
listed in this section. Section 166(d)
states that our pollutant-specific PSD
regulations ‘‘may contain’’ increments
or ‘‘other measures.’’ We interpret this
provision to allow EPA or the States to
employ approaches other than an
increment system, so long as such an
approach fulfills the ‘‘specific numerical
measures’’ criterion in section 166(c).
While an increment is the clearest
example of a specific numerical
measure for evaluating permit
applications because of the model
Congress established for PM and SO2,
the Act gives EPA the discretion to
employ other types of numerical
measures in PSD regulations for the
other pollutants listed in section 166,
such as ‘‘nitrogen oxides.’’ An
increment represents the allowable
marginal increase in air pollutant
concentration (measured in µg/m3.
Under this approach, the permit
applicant must conduct modeling to
determine whether or not its emissions
on a mass basis (e.g., tons) will result in
an air quality concentration increase in
excess of the increment. However,
another way to provide a numerical
measure for evaluating permits could
be, for instance, to establish a maximum
allowable level of emissions on a mass
basis (e.g., tons).
Under the latter approach, permit
applicants would have to show that
their emissions will not cause total
emissions in a given area to exceed the
maximum allowable level of emissions
established for that area. Under a State
planning approach, the State could
monitor the inventory of emissions from
all sources (new and existing) and only
issue a permit if the applicant’s project
would not cause emissions to exceed
allowable levels. Using a cap and trade
approach, EPA or the States could adopt
regional or statewide caps on emissions
of specific sources that could then be
allocated to States or individual sources
covered by the cap in the form of a
budget or allowance. Individual permit
applications would be evaluated against
the cap by determining whether the
applicant held a sufficient number of
allowances.
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2. Protect Air Quality Values
The third criterion in section 166(c)
broadly states that the regulations ‘‘shall
provide * * * protection of air quality
values’’ without identifying the air
quality values to be protected.
Legislative history indicates that the
term ‘‘air quality value’’ was used
interchangeably with the term ‘‘air
quality related value’’ (AQRV) regarding
Class I lands.4 Thus, we believe the term
‘‘air quality values’’ should be given the
same meaning as ‘‘air quality related
values.’’
The Act does not define AQRV,
except to note that it includes visibility.
Section 165(d)(1)(B). However, the
legislative history provides the
following explanation of AQRV:
The term ‘‘air quality related values’’ of
Federal lands designated as class I includes
the fundamental purposes for which such
lands have been established and preserved by
the Congress and the responsible Federal
agency. For example, under the 1916 Organic
Act to establish the National Park Service (16
U.S.C. 1), the purpose of such national park
lands ‘‘is to conserve the scenery and the
natural and historic objects and the wildlife
therein and to provide for the enjoyment of
the same in such manner and by such means
as will leave them unimpaired for the
enjoyment of future generations.’’
S. Rep. 95–127 at 36, reprinted at 3
Legislative History at 1410.
Thus, in 1996, the Agency proposed
the following definition of AQRV:
* * * visibility or a scenic, cultural,
physical, biological, ecological, or
recreational resource that may be affected by
a change in air quality, as defined by the
Federal Land Manager for Federal lands, or
by the applicable State or Indian Governing
Body for nonfederal lands.
61 FR 38250, 38322 (July 23, 1996). The
reference to State or Indian Governing
Body was to acknowledge that Congress
recognized in section 164(e) that such
areas also may have AQRVs to be taken
into consideration.
4 See S. Rep. 95–127, at 12, reprinted at 3
Legislative History at 1386, 1410 (describing the
goal of protecting ‘‘air quality values’’ in ‘‘Federal
lands—such as national parks and wilderness areas
and international parks,’’ and in the next paragraph
and subsequent text using the term ‘‘air quality
related values’’ to describe the same goal); id. at 35,
36 (‘‘The bill charges the Federal land manager and
the supervisor with a positive role to protect air
quality values associated with the land areas under
the jurisdiction of the [FLM]’’ and then describing
the statutory term as ‘‘air quality related values’’).
H.R. Report 95–564 at 532 (describing duty of
Administrator to consider ‘‘air quality values’’ of
the tribal and State lands in resolving an appeal of
a tribal or State redesignation, which is described
in the final bill as ‘‘air quality related values’’).
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3. Protect Public Health and Welfare
From Adverse Effects Notwithstanding
Attainment of NAAQS
The first goal and purpose in section
160 of the Act sets forth a broad mission
‘‘to protect public health and welfare
from any actual or potential adverse
effects which in the Administrator’s
judgment may reasonably be anticipated
to occur notwithstanding attainment
and maintenance of all national ambient
air quality standards.’’ The precise
meaning of this goal is somewhat
ambiguous because it appears to mirror
the legal standards applicable to the
promulgation of the primary and
secondary NAAQS. Under section
109(b) of the Act, the primary NAAQS
must ‘‘protect the public health’’ with
an adequate margin of safety (section
109(b)(1)) and the secondary NAAQS
must ‘‘protect the public welfare from
any known or anticipated adverse
effects’’ associated with ambient
concentrations of the pollutant (section
109(b)(2)). The term ‘‘welfare’’ is
defined in the Act to include ‘‘effects on
soils, water, crops, vegetation, manmade materials, animals, wildlife,
weather, visibility, and climate.’’
Section 302(h).
When applied as a relevant factor for
the content of PSD regulations for
specific pollutants under section 166(c)
of the Act, we do not construe this
language in section 160 to require EPA
to conduct a full NAAQS review every
time it establishes PSD regulations for a
pollutant. A NAAQS review is a
rigorous scientific process,5 and
5 The NAAQS process begins with the
development of ‘‘air quality criteria’’ under section
108 for air pollutants that ‘‘may reasonably be
anticipated to endanger public health or welfare’’
and that come from ‘‘numerous or diverse’’ sources.
Section 108(a)(1). ‘‘Air quality criteria’’ must reflect
the latest scientific knowledge on ‘‘all identifiable
effects on public health or welfare’’ that may result
from a pollutant’s presence in the ambient air. Id.
§ 7408(a)(2). The scientific assessments constituting
air quality criteria generally take the form of a
‘‘criteria document,’’ a rigorous review of all
pertinent scientific studies and related information.
The EPA also develops a ‘‘staff paper’’ to ‘‘bridge
the gap’’ between the scientific review and the
judgments the Administrator must make to set
standards. See Natural Resources Defense Council
v. EPA (‘‘NRDC’’), 902 F.2d 962, 967 (DC Cir. 1990).
Both documents undergo extensive scientific peerreview as well as public notice and comment. See
e.g., 62 FR 38654/1–2.
For each NAAQS review, the Administrator must
appoint ‘‘an independent scientific review
committee composed of seven members of the
National Academy of Sciences, one physician, and
one person representing State air pollution control
agencies,’’ known as the Clean Air Scientific
Advisory Committee (CASAC). Section
109(d)(2)(A). CASAC is charged with
recommending revisions to the criteria document
and NAAQS, and advising the Administrator on
several issues, including areas in which additional
knowledge is required to apprise the adequacy and
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Congress gave EPA 5 years to complete
this review. 42 U.S.C. 7409(d)(1).
However, under section 166(a) of the
Act, Congress gave EPA only 2 years to
establish PSD regulations for specific
pollutants. Furthermore, in cases where
NAAQS were not established as of 1977,
section 166(a) gave EPA 2 years after the
establishment of a NAAQS to
promulgate PSD regulations. This
indicates that Congress intended for
PSD regulations to be developed shortly
after establishment of a NAAQS and
before completion of the next NAAQS
review in 5 years. As a result, we do not
believe it is reasonable to interpret this
factor to require such a rigorous review
to establish PSD regulations. In
addition, as discussed further below, we
believe these statutory provisions
indicate that Congress intended for EPA
to develop PSD rules using the research
compiled when establishing or
reviewing a NAAQS.
In the specific context of the PSD
program, we construe this charge to
‘‘protect public health and welfare’’ to
require EPA to evaluate whether adverse
effects may occur as a result of increases
in pollution to ambient levels below the
NAAQS. If such effects may occur in
some areas of the country, then EPA
must consider how to establish PSD
regulations that protect public health
and welfare against such effects where
they may occur. However, we do not
interpret the PSD program to require
regulations that eliminate all adverse
effects that may result from increases in
pollution in attainment areas. The PSD
program is, as its title suggests, designed
to prevent ‘‘significant deterioration’’
from a baseline concentration. S. Rep.
95–127 at (3 LH at 1385) (‘‘This
legislation defines ‘significant
deterioration’ in all clean air areas as a
specified amount of additional
pollution. This definition is intended to
prevent any major decline in air quality
currently existing in clean air areas
* * *’’). That is, some decline in air
quality (relative to the baseline air
quality concentration) is permissible for
any particular area of the country that
is currently achieving the NAAQS, as
long as it is not ‘‘significant.’’ 6
basis of existing, new or revised NAAQS. Section
109(d)(2)(B), (C).
6 Of course, if the area is designated
nonattainment pursuant to section 107 of the Act
because the air quality is not attaining the NAAQS,
the PSD increments do not apply. Rather,
reductions in emissions must be implemented to
bring the area’s air quality into attainment with the
NAAQS, and, in the case of new sources, sufficient
offsetting emissions reductions must be obtained.
Sections 172(c) and 173(a) of the Act.
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4. Ensure Economic Growth Consistent
With Preservation of Existing Clean Air
Resources
The third goal and purpose set forth
in section 160 is to ‘‘insure that
economic growth will occur in a manner
consistent with the preservation of
existing clean air resources.’’ To some
extent, this goal of the PSD program
more specifically articulates the broader
purpose of the CAA, described in
section 101(b)(1) of the Act, to ‘‘protect
and enhance the quality of the Nation’s
air resources so as to promote the public
health and welfare and the productive
capacity of its population.’’ 42 U.S.C.
7401(b)(1). Sections 160(3) and 101(b)(1)
are similar in that both sections reflect
the goal to simultaneously protect air
quality and to foster economic growth.
Thus, in interpreting the meaning of
section 160(3) when used as a factor
applicable under section 166(c), we also
consider the broader purpose of the Act
set forth in section 101(b)(1).
The first part of this goal of the PSD
program set forth in section 160(3) (‘‘to
insure that economic growth will
occur’’) makes clear that the PSD
program is not intended to stifle
economic growth. However, the second
part of this goal indicates that economic
growth should ‘‘occur in a manner that
is consistent with the preservation of
existing clean air resources.’’ 42 U.S.C.
7470(3). Section 101(b)(1) indicates that
these goals are not necessarily
inconsistent because Congress sought to
‘‘protect and enhance the Nation’s air
resources so as to promote the public
health and welfare and the productive
capacity of [the Nation’s] population.’’
Thus, when considered in light of the
purpose of the Act set forth in section
101(b)(1), it is clear that section 160(3)
establishes the goal of the PSD program
to balance the promotion of economic
growth and the protection of clean air
resources.
Therefore, when applied as a guiding
factor for the content of pollutantspecific PSD regulations under section
166(c), we construe section 160(3) to
establish a balancing test between
fostering economic growth and
protecting: (1) AQRVs; (2) the public
health and welfare from adverse effects,
and (3) the air quality in parks and
special areas. When EPA employs an
area classification system in its section
166 regulations, all of these factors must
be weighed in each type of area (Class
I, Class II, and Class III). However, the
weight given to each factor may be more
or less depending on the area involved.
For example, economic growth may be
the most important factor in a Class III
area, but our PSD regulations for such
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areas should offer some level of
protection for existing clean air
resources. In a Class I area, our PSD
regulations should allow some level of
economic growth, even though
preservation of existing clean air
resources may be the dominant value for
these areas.
C. EPA’s Authority To Fulfill Section
166 Requirements by Granting States
Flexibility To Adopt Alternative
Measures in Their SIPs
Under section 110(a)(1) of the Act,
each State is required to submit a State
Implementation Plan (SIP) which
provides for implementation,
maintenance, and enforcement of the
primary and secondary NAAQS
established by EPA. All areas are
required to submit SIPs within certain
timeframes, and those SIPs must
include specified provisions identified
under section 110(a)(2) of the Act. SIPs
for nonattainment areas are required to
include additional specified control
requirements, as well as controls
providing for attainment of any revised
NAAQS and periodic reductions
providing ‘‘reasonable further progress’’
in the interim (see section 172(c)). For
attainment areas subject to the PSD
program, section 161 of the Act requires
that ‘‘each applicable implementation
plan shall contain emissions limitations
and such other measures as may be
necessary, as determined under
regulations promulgated under this part,
to prevent significant deterioration of air
quality in each region * * * designated
* * * as attainment or unclassifiable.’’
Thus, we have interpreted sections 166
and 161 to collectively require that EPA
promulgate a specific PSD regulatory
program for each pollutant identified in
section 166 (such as the existing NO2
increments and associated regulations),
and then to require the States to adopt
that program as part of their SIPs.
We view the PSD program to be a
growth management program that is
intended to limit the deterioration of air
quality beyond baseline levels that may
be caused by the construction of major
new and modified sources. We do not
interpret the PSD provisions to
authorize us to direct States in their
SIPs to achieve reductions in emissions
from existing sources. However, we
recognize that the growth management
goals of PSD may also be fulfilled when
the States adopt controls on existing
sources that would reduce emissions
and allow growth from new sources and
major modifications to existing sources
without causing significant
deterioration. Under the increment
approach, we have previously
recognized that States may choose to
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require reductions from existing sources
in order to expand the increments and
allow for more growth under the PSD
program.7 However, we have never
required States to do so because, in the
absence of an increment violation, we
do not believe section 166 and other
provisions in part C give us the legal
authority to mandate such reductions
for PSD purposes. Consistent with these
authorities, in addition to requiring
States to adopt a specific PSD program
for NOX promulgated under section 166
as part of their SIPs, we believe we
could also give States the flexibility to
develop their own programs that EPA
could review to determine if the State
program meets the requirements of
section 166(c) and 166(d) of the Act. If
a State adopts a program that meets the
criteria of sections 166(c) and 166(d), we
believe section 166 would give us the
authority to allow the State to
implement that program in lieu of any
specific program (such as one that may
include increments) that EPA might
adopt under section 166. Thus, we think
one option for fulfilling our obligation
to promulgate pollutant-specific
regulations for NOX under section 166
would be to adopt regulations that
establish a procedure for States to
submit their own programs to satisfy
section 166. These regulations would
contain criteria that would guide EPA’s
evaluation of whether a State program
contains ‘‘other measures’’ that are
sufficient to satisfy the requirements of
sections 166(c) and 166(d) and to
operate in lieu of an EPA-promulgated
program.
V. Health and Welfare Effects of NOX
‘‘Nitrogen oxides’’ is the generic term
for a group of highly reactive gases that
contain nitrogen and oxygen in varying
amounts. The high-temperature
combustion of fossil fuels, primarily
from electric utilities and mobile
sources, is a major contributor to the
formation of nitric oxide (NO) and NO2.
Most NOX from combustion sources are
emitted as NO (about 95 percent); the
remainder are primarily NO2. Emissions
of NO are rapidly oxidized in the
atmosphere to produce even more NO2.8
Nitrogen oxides 9 play a major role in
the formation of ozone and PM
7 43 FR 26380, 26381 (June 19, 1978) (‘‘States can
expand the available PSD increments by requiring
emissions reductions from existing sources.’’)
8 Because NO is readily converted to NO in the
2
atmosphere, the emissions of NOX reported by EPA
assumes NOX in the form of NO2. In predicting
ambient impacts that may result from emissions of
NOX, all NOX initially is assumed to be emitted
from sources as NO2. (40 CFR part 50 app W sec.
6.2.4.)
9 Seven oxides of nitrogen are known to occur in
the atmosphere: nitric oxide (NO), nitrogen dioxide
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(nitrogen-bearing particles and acid
aerosols), each with their own set of
adverse health and welfare effects.10 For
example, nitrate particles contribute to
visibility impairment and regional haze
and nitrates are a major component of
acidic deposition. Emissions of NOX
also contribute to nitrates in drinking
water, nitrogen loadings to aquatic
(eutrophication) and terrestrial
(nitrification)11 ecosystems, toxics,
stratospheric ozone depletion, and
global climate change.
Reduced nitrogen compounds, such
as ammonia (NH3) (derived largely from
emissions from livestock waste as well
as those associated with the application
of fertilizer to the ground) and
ammonium (NH4¶), are also important
to many of the public health and
environmental impacts associated with
atmospheric nitrogen compounds. It is
important to recognize that some forms
of NOX are produced naturally (via
lightning, soils, wildfires, stratospheric
intrusion, and the oceans) and also can
play a role in the cycling of nitrogen
through the ecosystem. Such varied
origins of nitrogen in the atmosphere
add to the difficulty of determining the
specific source contributing to the total
nitrogen concentration and, therefore,
make it difficult to design an emissions
control strategy for reducing the
nitrogen contribution in a particular
area.
A. Scope of Effects EPA Proposes To
Consider
In order to evaluate our pollutantspecific PSD regulations for NOX under
section 166(c), we must first define the
scope of effects that are relevant to our
analysis. Although emissions of NOX
contribute to a range of direct and
indirect effects on health, welfare, and
AQRVs, we believe our review should
focus on those effects that were
(NO2), nitrate (NO3·), nitrous oxide (N2O),
dinitrogen trioxide (N2O3), dinitrogen tetroxide
(N2O4) and dinitrogen pentoxide (N2O5).
10 The term ‘‘welfare’’ is defined in the Act to
include, inter alia, ‘‘effects on soils, water, crops,
vegetation, man-made materials, animals, wildlife,
weather, visibility, and climate.’’ Section 302(h).
11 It should be noted that nitrification can be a
beneficial process in many instances. Nitrification
(a bacterially driven process that converts
ammonium to nitrite) can occur productively in
manure piles, during sewage processing, in soil,
and in marine environments in the oxygenated
water column above anaerobic sediments or within
the surface of oxidized layers of sediments.
Nitrification becomes adverse when it is
accompanied by ‘‘nitrogen saturation,’’ a condition
that can arise in terrestrial ecosystems from the
long-term chronic effects of nitrogen deposition or
loading, where nitrogen inputs into an ecosystem
exceed the ability of plants and soil organisms to
utilize it so that it begins to leach nitrite out of the
soil into streams and other water bodies.
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considered by EPA in the development
of the NAAQS for NO2.
EPA believes that this approach is
appropriate because the need to develop
PSD rules is tied to the existence of the
NAAQS. As the court in EDF v. EPA
acknowledged ‘‘the ambient standards
are the basic measure of air quality
under the [Clean Air Act] and the
controlling standards by no means
exclude any value that is the subject of
focus under the PSD provisions.’’ 898
F.2d at 190 (emphasis in original). Thus,
the health and welfare effects that were
evaluated by EPA when it established
the NAAQS should also be considered
when EPA establishes regulations under
section 166 to protect against significant
deterioration of air quality from NOX
emissions.
This view is supported by the
provisions of section 166 which make
clear that EPA is to establish PSD
regulations (including an increment, if
appropriate) under this provision after
the establishment of a NAAQS for the
applicable pollutants. In 1971, EPA first
established a single standard for NO2 as
both the primary and secondary NAAQS
addressing NOX. 36 FR 8186 (April 30,
1971). Congress then passed section 166
of the Act in 1977 and gave EPA 2 years
to complete its study and promulgate
PSD regulations for ‘‘nitrogen oxides.’’
42 U.S.C. 7476(a). In addition, for
pollutants for which a NAAQS had not
been promulgated by August 7, 1977,
Congress gave EPA 2 years from the
promulgation of such standards to
establish PSD regulation under section
166 of the Act. Id. The establishment of
PSD regulations which may include
increments must necessarily follow the
NAAQS because the NAAQS provides
the benchmark against which we are to
judge ‘‘significant deterioration’’ of air
quality.
Although we propose to use the range
of effects considered in setting the
NAAQS to define the bounds of our
analysis, we are also mindful that the
court in EDF v. EPA rejected use of the
NAAQS as the ‘‘sole basis’’ for deriving
the increment. 898 F.2d at 190.
However, in this action, we propose to
focus not simply on the level of the
NAAQS as a legal standard, as we did
in 1988, but to further consider the
health and welfare effects that EPA
evaluated to establish the NAAQS.
Rather than considering those effects in
relation to the standards set forth in
section 109, we now evaluate those
effects in relation to the factors in
sections 166(c) and 160 of the Act. The
court held that we could not rely solely
on the NAAQS itself to establish
increments because of the emphasis in
sections 166(c) and 160 on special
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8889
considerations—such as national
wilderness areas—whose special values
may be reflected in the NAAQS but are
not necessarily the only factors that
determine the level of the NAAQS. See
898 F.2d at 190. Thus, within the field
of effects that EPA found relevant when
establishing the NAAQS, we narrow our
inquiry here to focus on the special
considerations of PSD and those effects
that may occur in some areas
notwithstanding attainment of the
NAAQS.
As noted above, both photochemical
oxidants (ozone) 12 and PM 13 are
formed in part by reactions of NOX
emissions with other pollutants in the
atmosphere. Thus, the question arises
whether the PSD regulations for NOX
must also address the ozone and PM
impacts. Because section 166(a) directs
EPA to separately promulgate pollutantspecific PSD regulations for
photochemical oxidants (i.e., ozone), we
believe the duty to promulgate
increments for ‘‘nitrogen oxides’’ does
not include consideration of ozone.14
We believe that Congress did not
intend for EPA to establish duplicative
PSD regulations. Several pollutants are
identified in section 166(a) for the
promulgation of regulations to ‘‘prevent
the significant deterioration of air
quality which would result from the
emissions of such pollutants.’’ In
addition to ‘‘nitrogen oxides,’’ the
statute lists ‘‘photochemical oxidants’’
and any pollutants for which NAAQS
are later promulgated. Increments for
PM10 are separately authorized in
section 166(f).
In addition, we believe it would be
unreasonable to establish pollutantspecific PSD regulations to protect
against the effects of ozone without
considering the other major precursor
12 Ozone is the oxidant found in the largest
quantities in the atmosphere. The EPA promulgated
NAAQS for photochemical oxidants in 1971. The
chemical designation of the standard was changed
in 1979 from ‘‘photochemical oxidants’’ to ozone.
See 44 FR 8202 (February 8, 1979).
13 Particulate matter (PM) is composed of directly
emitted particles and secondarily formed particles.
Secondary particulates are produced from gaseous
pollutants, mainly NOX, SO2, ammonia, and some
VOCs. Emissions of NOX can result in the formation
of particulate nitrates whose contribution to fine
particles varies depending on geographic location
and other criteria.
14 In the 1988 final preamble adopting the NO
2
increments, we gave limited consideration to
whether limiting increases of NOX emissions would
worsen ozone ambient concentrations, in response
to comments raising this issue. 53 FR at 40668. We
did not, however, attempt to set the NO2 increments
to address ozone public health and welfare impacts,
nor do we believe that is required here, for the
reasons stated above. Increments for ozone have not
been established because of the technical difficulty
associated with predicting ambient concentration
changes resulting from a single stationary source. 61
FR 65764, 65776 (Dec. 13, 1996).
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for ozone—volatile organic compounds.
Any PSD regulation attempting to
mitigate the ozone impacts from NOX,
notwithstanding the ozone NAAQS,
would be unfounded without also
addressing this significant component.
Thus, we believe the contribution of
NOX to the formation of ozone should
be considered only in the context of the
establishment of pollutant-specific PSD
regulations for ozone.
For similar reasons, we believe the
duty to promulgate PSD regulations for
‘‘nitrogen oxides’’ under section 166 of
the Act does not include a requirement
to consider effects attributable to PM.
Instead, Congress established
increments for PM (then measured as
total suspended particulate or TSP) and
authorized EPA to replace the TSP
increments with increments for PM10.
See CAA sections 163 and 166(f). Thus,
we believe it would be inappropriate to
promulgate pollutant-specific
regulations for NOX based on its
transformation into PM. Regulations for
NOX that address PM effects in such a
narrow manner (i.e., nitrates 15 only)
could potentially affect the stringency of
the PM increments and considerations
regarding the baseline concentration
and baseline date. Additionally, like
ozone, PM has several precursors, of
which NOX is only one. Any PSD
strategy for PM should consider both
direct PM emissions and all of the
regulated precursors instead of placing
disproportionate emphasis on only one
component of the pollutant. In a
separate notice, EPA intends to consider
options for regulating precursors to
PM2.5.
B. Data Included in Review
Our review of the available scientific
and technical information focuses
primarily on the health and welfare
information contained in the 1993
Criteria Document for NOX and the 1995
OAQPS Staff Paper used for the periodic
review of the NO2 NAAQS completed in
1996. As described below, we have also
considered information contained in
more recent studies, particularly
concerning the types of effects on
ecosystems associated with atmospheric
nitrogen deposition because the Act
does place an emphasis on protection of
air quality values and national parks
and other special areas of national or
regional interest.
The court’s opinion in EDF v. EPA did
not indicate what data set EPA should
15 NO may be transformed to nitrate particulates
2
by means of chemical reactions in the atmosphere.
Nitrate is a major constituent of atmospheric PM.
Due to limited scientific literature addressing the
health impacts of nitrates, exposure currently is
analyzed as exposure to fine PM. (NAPAP, 1998.)
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use in its review under the statutory
criteria in sections 166(c) and 166(d).
When EPA promulgated the NO2
increments in 1988, the health and
welfare information used for completing
the periodic review of the NO2 NAAQS
(50 FR 25532, June 19, 1985) was
contained in EPA’s 1982 Criteria
Document for NOX. The same document
represented the Agency’s latest official
documentation of health and welfare
effects when the 1988 increments were
challenged by Environmental Defense.
In general, we believe that it is
appropriate to rely on the latest
information used for promulgating or
reviewing the NAAQS in order to
evaluate the effectiveness of a set of
increments or other PSD regulations for
the same pollutant. This is because,
under normal circumstances, the Act
provides that EPA promulgate new PSD
regulations under section 166, including
new increments if appropriate, within 2
years from the promulgation of any
NAAQS after 1977. 42 U.S.C. 7476(a). In
such instances, the health and welfare
information used for the setting of the
NAAQS would also be ‘‘current’’ for
purposes of establishing pollutantspecific PSD regulations.
The record of information used for the
most recent periodic review of the NO2
NAAQS includes the 1993 Criteria
Document and 1995 Staff Paper. This
information was used in 1996 to carry
out the required periodic review of the
NO2 NAAQS and to conclude that the
existing primary and secondary NO2
NAAQS should be retained in the
original form. 61 FR 52852 (October 8,
1996).
The most recent review of the NO2
NAAQS contains information that was
not part of the scope of the previous
NAAQS review. Specifically, the 1993
Criteria Document and 1995 Staff Paper
considered as part of the secondary
standard review ‘‘short- and long-term
effects of nitrogen deposition on
biological, physical and chemical
components of ecosystems and the
resulting effect of changes to these
components on ecosystem structure and
function as well as the traditional issue
of visibility impairment, and materials
damage.’’ The expanded scope is
particularly relevant to the types of
effects that should be used to consider
the effectiveness of the PSD increments.
While we believe that it is in keeping
with congressional intent to rely in the
ordinary case on only the information
used in the most recent NAAQS review
when establishing pollutant-specific
PSD regulations under section 166, the
situation we face here with NOX is
unique. Considerable time has passed
since the 1996 review of the NO2
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NAAQS. Thus, in this unique case
where we are reevaluating the NO2
increment, we have also evaluated
information contained in a number of
more recent studies, published since
completion of the last NAAQS review,
to determine whether there have been
significant advances in scientific and
technical information. However, our
review of the post-1996 scientific and
technical information does not represent
the level of effort appropriate for the
development of a criteria document.
Nevertheless, we believe our review was
sufficient to determine that there has
not been a substantial advance in
scientific understanding of the ambient
pollutant concentration levels at which
adverse effects may occur as a result of
NOX emissions. Thus, we believe the
research summarized in the most recent
criteria document and Staff Paper
remains valid and relevant for purposes
of this review. Although the more recent
data augment our understanding of the
effects that may be caused by emissions
of NOX, they do not provide significant
new information on the specific ambient
air pollutant concentrations that may
ultimately cause or contribute to these
effects. Thus, the data concerning
pollutant impacts associated with NOX
do not provide sufficient information
from which it would be possible to
conclude that the levels of the existing
NO2 increments are inadequate for
purposes of the nationwide PSD
program.
C. Analysis of Effects
This section contains a summary of
the health and welfare effects reviewed
by EPA as part of the reconsideration of
the pollutant-specific PSD regulations
for NOX. These effects are within the
scope of effects reviewed by EPA as part
of its decision in 1996 to retain the
existing primary and secondary NO2
NAAQS. The objective of this technical
review is to determine whether there is
any compelling basis for proposing to
modify the original NO2 increments,
which were based on the ‘‘percentageof-NAAQS’’ approach, in order to
ensure that we promulgate pollutantspecific PSD regulations for NOX that
adequately protect air quality values,
parks and special areas, and health and
welfare from adverse effects which may
occur in some areas notwithstanding
compliance with the NAAQS.
1. Health Effects
In 1996, EPA announced its
conclusions that the current primary
ambient air quality standard for NO2,
which is in the form of an annual
standard for NO2, ‘‘appears to be both
adequate and necessary to protect
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human health against both long- and
short-term NO2 exposures.’’ 61 FR
52852. In reaching this conclusion, EPA
considered a variety of acute (shortterm) and chronic (long-term) health
effects associated with exposure to NO2
concentration.16 Some of the most
serious health effects reviewed by EPA
were shown to occur at significantly
higher exposure concentrations than are
allowed by the NAAQS; other health
effects, however, were found to occur at
levels near the NAAQS. For our review
purposes herein, only the adverse health
effects that were found to occur at levels
at or near the NAAQS are being
considered.17
The health effects of most concern at
ambient or near-ambient concentrations
of NO2 with short-term (e.g., less than 3
hours) exposure include mild changes
in airway responsiveness (airway
constriction and narrowing) and
decrease in pulmonary function. In
addition, there is some evidence of
increased respiratory illnesses among
children associated with long-term, lowlevel exposure to NO2. Each of these
effects is summarized below.
While there is little evidence to show
that healthy individuals experience
increases in airway responsiveness
when exposed to NO2 concentrations
below 1.0 ppm, clinical studies of
asthmatics have reported evidence of
increased airway narrowing at relatively
low concentrations (mostly within the
range of 0.2 to 0.3 ppm NO2) at shortterm exposures of less than 3 hours.
However, such responses did not appear
to cause airway inflammation and were
fully reversible. In addition, the
exposure concentrations studied
exceeded the ambient levels typically
monitored in areas that meet the annual
NAAQS.
Small changes in pulmonary function
have been observed in asthmatics at
NO2 concentrations generally ranging
between 0.2 and 0.5 ppm NO2 either at
rest or following periods of exercise.
Some findings of airway resistance
occurred in mild asthmatics exposed to
concentrations as low as 0.1 ppm NO2
at rest. However, EPA concluded that
this finding was not considered
statistically significant. As above, the
concentrations related to these effects
exceed the levels typically monitored in
areas meeting the NAAQS.
Increases in respiratory illnesses in
children 5 to 12 years old resulting from
exposure typically averaging over a 2week period were reported in a number
of epidemiological studies investigating
effects of indoor exposure to NO2
emitted from gas stoves. In these
studies, NO2 concentrations were
estimated in terms of two-week average
NO2 exposures, where mean weekly
exposure concentrations in bedrooms
were predominantly between 0.008 and
0.065 ppm NO2. The EPA noted various
limitations with these studies, however,
that made it extremely difficult to
extrapolate the results in a manner that
would yield quantitative estimates of
health impacts for outdoor exposure to
NO2.
16 Based on the 1993 Criteria Document used for
the decision in 1996 to retain the existing NO2
NAAQS, EPA reaffirmed its previous conclusion
that NO2 is the only oxide of nitrogen sufficiently
widespread and commonly found in ambient air at
high enough concentrations to be a matter of public
health concern. 60 FR 52878, October 11, 1995.
17 For the purposes of this review, we are only
summarizing some of the adverse health effects that
were identified during EPA’s periodic review of the
NO2 NAAQS in 1996. A detailed discussion of
pertinent studies can be found in the 1993 Criteria
Document and the 1995 Staff Paper.
a. Direct Welfare Effects
The periodic review of the NO2
NAAQS, leading to EPA’s final decision
published in 1996, expanded the scope
of coverage over the previous periodic
review in that it included new
environmental considerations, set forth
by the Clean Air Act Amendments of
1990 (1990 Amendments), not included
in the earlier review. In addition to the
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2. Welfare Effects
In its 1996 review of the NAAQS, EPA
concluded that the ‘‘available scientific
and technical evidence * * * does not
provide an adequate basis for setting a
separate secondary standard for NO2’’ to
address the welfare effects considered
by EPA. 61 FR 52855. In addition,
because of the multiple causes and
regional character of many of the
welfare effects that may be associated
with NOX emissions, the Administrator
concluded that ‘‘adoption of a
nationally uniform secondary standard
would not be an effective approach to
addressing them.’’ Id. Thus, EPA
adopted a secondary standard for NO2
that is the same as the primary standard.
However, as discussed earlier, the
goals and purposes of the PSD program
include protection of welfare, air quality
values and areas of special national and
regional interest (national parks,
national wilderness areas, etc.).
Nitrogen dioxide and other nitrogen
compounds have been associated with a
wide range of environmental effects.
Thus, EPA has reviewed the information
on welfare effects to determine whether
there is any basis for modifying the
existing NO2 increments or to establish
an alternative regulatory framework in
order to provide additional protection
notwithstanding attainment of the
NAAQS in PSD areas.
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environmental features identified for
protection by the secondary standard in
the definition of public welfare (see
section 302(h) of the Act), the 1990
Amendments expressed a new
determination on the part of Congress to
investigate through research ‘‘short-term
and long-term causes, effects, and trends
of ecosystems damage from air
pollutants * * *’’ (see section 301(e) of
the Act). Thus, in addition to the
traditional issues of visibility
impairment, and vegetation and
materials damage, EPA’s most recent
periodic review of the NO2 NAAQS
addressed as part of the secondary
standard review short- and long-term
effects of nitrogen deposition on
biological, physical and chemical
components of ecosystems and the
resulting effect of changes in these
components on ecosystems structure
and function.
Information contained in the 1993
Criteria Document, not available in the
previous criteria document, indicated
that single exposures to NO2 for less
than 24 hours can produce effects on
growth, development, and reproduction
of plants. However, the data did not
suggest significant effects at or below
the current ambient standards level.
Instead, the observed effects generally
occurred at concentrations greatly
exceeding the ambient levels of NO2
measured in the U.S. Some studies have
shown that NO2 in combination with
other pollutants (i.e., SO2, ozone) can
increase plant sensitivity, thus lowering
concentration and time of exposure
required to produce injury/growth
effects. Again, however, the pollutant
concentrations used in these
experimental studies were well above
those observed in the ambient air and at
a frequency of occurrence not typically
found in the U.S.
Nitrogen dioxide has been
qualitatively associated with various
adverse effects on materials. For
example, exposure to NO2 may
contribute to: Enhancing the fading of
dyes; diminishing the strength of
fabrics, plastics and rubber products;
assisting the corrosion of metals; and
reducing the useful life of electric
components, paints, and masonry.
Compared to studies on sulfur oxides,
however, there is limited information
available quantifying the effects of NO2
or other nitrogen compounds. The
available evidence shows that it is
difficult to distinguish a single causative
agent for observed damage because
many agents, together with a number of
environmental stresses, act on the
surface of materials over time.
Another potential direct effect of NO2
is visibility impairment. NO2 and other
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pollutants can degrade the visual
appearance of distant objects and reduce
the range at which they can be
distinguished from the background. NO2
appears as a yellow to reddish-brown
gas because it absorbs blue light,
allowing red wavelengths to reach the
eye.
The discoloration effect is most
noticeable as local scale or ‘‘reasonably
attributed impairment,’’ defined as a
coherent, identifiable impairment,
which can be seen as an optical entity
(plume) against the background sky or a
distant object. NO2 does not normally
contribute significantly to haze in
remote areas, because of its high
reactivity and relatively short lifetime in
the atmosphere. Large-scale ‘‘regional
haze’’ is more commonly associated
with the light-scattering properties of
PM, including nitrate PM formed by
chemical reactions involving NO and
NO2 with other substances in the
atmosphere, and is discussed below as
an indirect effect of NO2.
As reported in the 1995 Staff Paper (p.
87), the 1993 Criteria Document
indicated that less than 0.1 ppm-km
NO2 is sufficient to produce a color shift
that is distinguishable in carefully
controlled, color matching tests.
However, at concentrations below 0.01
ppm (approximately the concentration
increase allowed by the Class II
increment for NO2), area-wide impacts
of NO2 absorption are not considered
important.18 In addition, some studies
have shown that brownish discoloration
can result from particles alone, thus
making it difficult to determine a
reliable relationship between groundlevel concentrations of NO2 at any given
point and discoloration caused by
particles which may also be in a
source’s plume. The 1995 Staff Paper
noted that despite the known lightabsorbing qualities of NO2, ‘‘there are
relatively little data available for judging
the actual importance of NO2 to visual
air quality.’’
b. Indirect Welfare Effects
Various other welfare effects
associated with NO2 of environmental
concern are indirect effects that NO2
may have on ecosystems. These indirect
effects occur following the
transformation of ambient NO2 to other
nitrogen compounds by chemical
reactions in the atmosphere and the
transfer of these compounds from the
atmosphere to other media through a
process known as atmospheric nitrogen
deposition (nitrogen deposition).
Nitrogen deposition is the process by
18 ‘‘Protecting Visibility: An EPA Report to
Congress,’’ OAQPS, October, 1979.
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which nitrogen in airborne compounds
is transferred to a variety of surfaces,
e.g., water, soil, vegetation, and other
materials.
In terrestrial or agricultural systems,
for example, that are nitrogen limited,
some amount of nitrogen deposition can
enhance growth of some forest species
and crops. However, in areas where
deposition occurs in excess of plant and
microbial demand (also known as
nitrogen saturation) the added nitrogen
can disturb the nitrogen cycle,
contributing to such adverse effects as
increased plant susceptibility to some
natural stresses and modification of
interplant competition.
To have an effect on a particular
ecosystem, nitrogen that has been
released to the atmosphere must enter
the ecosystem by either wet (rain or
snow), dry (transfer of gases or
particles), or occult (fog, mist or cloud)
deposition. Nitrogen deposition occurs
primarily as nitrates, which are formed
in the atmosphere by the oxidation of
NO and NO2, or as ammonia, which is
released by agricultural or soil microbial
activity. When the nitrogen transfer
process involves acids (e.g., nitric acid)
or acidifying compounds, the deposition
process is referred to as ‘‘acidic
deposition.’’ The adverse welfare effects
associated with both types of nitrogen
deposition are discussed in greater
detail in the subsections below.
In the 1995 Staff Paper assessing the
scientific and technical information
contained in the 1993 Criteria
Document, it was reported that little, if
any, research had been initiated to
determine what percentage of total (wet
and dry) nitrogen deposition can be
attributed to emissions of stationary and
mobile sources of NOX. The EPA did,
however, estimate at that time that
approximately one-third to one-half of
the emissions of NOX in the U.S. are
removed by wet deposition, and it was
generally assumed that dry deposition
was equal to wet deposition for areas
directly adjacent to emissions sources.
The same assumption for wet deposition
could not be made in receptor locations
remote from the emissions sources.
More recently, at least one study has
been published reporting on the
relationship between emissions of NOX
and nitrate concentrations (and
deposition) in the eastern U.S. The
results of this study suggest linearity,
specifically, that a reduction in NOX
emissions may reduce NO3·
concentrations and acidic precipitation
(wet deposition) with an efficiency
ranging between 75 and 95 percent
(Butler, 2003). The study was limited to
the eastern U.S., and left unanswered
the percentage contribution of total NOX
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emissions to the total nitrogen
deposition.
Studies such as this can provide
potentially useful information to help
estimate the relative benefits (in terms
of anticipated reductions in NO3·
deposition) resulting from different NOX
emissions control strategies. Similarly,
such information could prove useful in
evaluating the relationship between
different levels of allowable ambient
NO2 concentration increases (i.e., PSD
increment levels) and corresponding
total nitrogen deposition rates.
Unfortunately, there are additional
criteria that would need to be studied in
order to be able to adequately evaluate
this relationship and associated
environmental effects.
To further complicate matters, dry
deposition differs from wet deposition
in that a sample taken at a particular
location cannot be assumed to represent
the rate of dry deposition of the area as
a whole. Instead, dry deposition is
driven by surface properties that are
site-specific. Thus, a regionally
representative average rate of dry
deposition cannot be readily derived
from information obtained from a single
location (NOAA, 2004).
The following subsections summarize
the various indirect effects of NO2 on
ecosystems, including terrestrial
systems (i.e., plant communities),
wetlands, and aquatic systems. The EPA
believes that the effects described are
potentially relevant to an evaluation of
the pollutant-specific PSD regulations
for NOX because these effects have been
observed in areas of the country that are
attaining the NAAQS.
(1) Terrestrial ecosystems. Soils are
the largest pool of nitrogen in forest
ecosystems, although such nitrogen is
generally not available for plants until it
has been mineralized by bacteria (Fenn,
1998). Another important source of
nitrogen is atmospheric wet and dry
deposition, which often has a fertilizing
effect on terrestrial ecosystems,
accelerating plant growth. While this
effect can sometimes be considered
beneficial, nitrogen deposition may also
cause or contribute to significant
adverse changes in terrestrial
ecosystems, including soil acidification,
increase in soil susceptibility to natural
stresses, and alterations in plant species
mix.
When excess nitrogen input causes
soil acidification, it can alter the
availability of plant nutrients (i.e.,
calcium and magnesium) and expose
tree roots to toxic levels of aluminum
and manganese, thereby having an
adverse effect on tree growth. It can also
lead to the mobilization of aluminum
from the soil as nitrates are leached
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from the soil and transported to
waterways, where the aluminum can
exhibit toxic effects to aquatic
organisms.19
Air pollution is not the sole cause of
soil change; many studies have shown
that acidic deposition is not a necessary
condition for the presence of extremely
acidic soils. High rates of acidification
are occurring in less polluted regions of
western U.S. because of internal soil
processes, such as tree uptake of nitrate
and nitrification associated with
excessive nitrogen fixation. Although
nitrogen deposition can accelerate the
acidification of soils, the levels of
nitrogen necessary to produce
measurable soil acidification are quite
high. The 1993 Criteria Document
indicated that, at that time, nitrogen
deposition had not been directly
associated with the acidification of soils
in the U.S. More recent information
suggests that in parts of the Northeast,
for example, acid deposition has
resulted in the accumulation of sulfur
and nitrogen in the soil beyond the
levels that forests can use and retain,
and has accelerated the leaching of base
cations, such as calcium and
magnesium, that help neutralize acid
deposition. (Driscoll, 2001.) Some
western forest areas may also be
experiencing nitrogen saturation
conditions, although the role of nitrogen
deposition may vary from one location
to another (Fenn, 1998, 2003).
Aside from the effects of soil
acidification, some studies have shown
that increased nitrogen deposition can
alter tree susceptibility to frost damage,
insect and disease attack, and plant
community structure. However, other
studies have not shown that similar
results occur. In all, the studies
evaluated in the 1993 Criteria Document
which focused on the impact of
excessive inputs of nitrogen in forest
ecosystems showed mixed results. The
long response time of trees to
environmental stresses has made it
difficult to fully understand how acid
rain may affect trees. It is also difficult
to isolate the possible effects of acid rain
from other stresses resulting from other
natural and anthropogenic origins.
However, more recent studies appear to
provide some evidence that acid
deposition has caused the death of red
spruce trees, particularly at higher
19 Aluminum from soil seldom appears in aquatic
systems because natural aluminum minerals are
insoluble in the normal pH range of natural waters.
However, the term ‘‘aluminum mobilization’’ refers
to the the conversion of aluminum in acidic soils
into dissolved forms and its transport, as runoff or
subsurface flow, to water systems. Mobilized
aluminum can then alter the acid/base property of
natural water systems (Wang, 2004).
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elevations in the Northeast by
decreasing cold tolerance, and may be
in part responsible for the extensive loss
of sugar maple in Pennsylvania.
(Driscoll, 2001.)
Finally, in terrestrial systems in
which the pre-existing balance is
marked by a competition among species
for the available nitrogen, additional
nitrogen inputs, such as nitrogen
deposition, may bring about an
alteration of the species mix. That is, a
displacement of one kind of vegetation
(e.g., plants, grasses) with another may
occur. While the 1995 Staff Paper noted
that there were no documented accounts
of terrestrial ecosystems undergoing
species shifts due to nitrogen deposition
in the U.S., recent research provides
some evidence suggesting that elevated
nitrogen deposition can contribute to
shifts of species compositions (e.g.,
Allen, 1998; Bowman, 2000).
(2) Wetlands. Wetlands (e.g., swamps,
marshes, bogs) are lands where
saturation with water is the dominant
factor determining the nature of soil
development and the types of plants
and animal communities living in the
soil and on its surface. These areas
function as habitats for plant and
wildlife (among other useful
environmental purposes), including
many rare and threatened plant species.
Some of these plants adapt to systems
low in nitrogen or with low nutrient
levels. Long-term studies (greater than 3
years) of increased nitrogen loadings to
wetland systems in European countries
have reported that increased primary
production of biomass can result in
changes of interplant competition. The
1995 Staff Paper reported that, based on
the evidence reviewed in the 1993
Criteria Document, ‘‘the staff believes
we can anticipate similar effects from
atmospheric nitrogen deposition in the
United States * * *.’’ However, EPA
found no documentation providing
sufficient evidence that such species
changes have occurred or were
occurring at the time in the U.S.
(3) Aquatic ecosystems. Nitrogen
deposition may adversely affect aquatic
ecosystems as a result of either
acidification or eutrophication. Both
processes can cause a reduction in water
quality that makes the body of water
unsuitable for many aquatic organisms.
The basic concern is that deposition of
nitrates alters the availability of nitrogen
to organisms (e.g., algae, fish,
submerged vegetation, and amphibian
and aquatic vertebrate communities)
and causes changes in species
composition within the system. In
addition, the affected water can become
unfit for human consumption.
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The 1995 Staff Paper indicated that
growing evidence supported the
concern that the impact of nitrogen
deposition on sensitive aquatic systems
‘‘may be significant.’’ Atmospheric
nitrogen can enter lakes and streams
either as direct deposition to the water
surfaces or as nitrogen deposition to the
watershed of which they are a part. In
some cases, nitrate may be temporarily
stored in snow packs from which it is
subsequently released in more
concentrated form in snow melt. In
other cases, nitrogen deposited to the
watershed may subsequently be routed
through plants and soil microorganisms
and transformed into other inorganic or
organic nitrogen species which, when
they reach the water system, are only
indirectly related to the original
deposition. In addition to the
contribution of nitrogen from
anthropogenic sources, recent studies
suggest that nitrogen released from the
weathering of nitrogen-bearing bedrock,
not commonly considered in the
biogeochemical cycling of nitrogen, may
contribute a ‘‘surprisingly large
amount’’ of nitrate to natural waters.
(Dahlgreen, 2002.)
Acidification may occur in two ways:
Chronic (long-term) acidification and
episodic (short-term or seasonal)
acidification. Episodic acidification is
more likely to be the primary problem
in most situations, with chronic
acidification occurring mainly where
excessive nitrogen saturation exists.
(NAPAP, 1998.) The main concern with
acidification of aquatic ecosystems is
associated with freshwater systems.
Acidification impairs the water quality
of lakes and streams by lowering the pH
levels, decreasing acid-neutralizing
capacity, and increasing aluminum
concentrations. (Driscoll, 2001.) High
levels of aluminum, as well as increased
acidity, create unfit conditions for
habitat and cause the water to be unfit
for human consumption. Acid
deposition may also increase the
conversion of mercury to organic
(methyl) mercury in lakes where it is
absorbed by aquatic organisms and
leads to increasing concentrations in the
food chain. Human consumption of fish
containing high levels of methylmercury
can lead to problems with the central
nervous system.
Regions of North America differ in
their sensitivity to acidic deposition and
in the amount of acidic deposition they
receive. Some parts of the eastern U.S.
are highly sensitive and chronically or
episodically receive damaging
concentrations of acidic deposition. For
example, a recent report indicates that
41 percent of lakes in the Adirondack
Mountain region of New York and 15
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percent of lakes in New England show
evidence of either chronic or episodic
acidification, or both. (Driscoll, 2001.)
Other sensitive regions, such as the
western U.S., are unlikely to suffer
adverse chronic effects but may
experience acidic conditions more on an
episodic basis. Certain high-elevation
western lakes, in particular, are subject
to episodes of acidic deposition.
Eutrophication generally is a natural
process by which aquatic systems are
enriched with the nutrients, including
nitrogen, that are presently limiting for
primary production in that system.
However, this process can be
accelerated by increased nutrient input
resulting from anthropogenic sources,
e.g., agricultural runoff, urban runoff,
leaking septic systems, sewage
discharge. Studies have also shown that
nitrogen deposition may directly and
indirectly play a role in accelerated
eutrophication. When nitrogen is a
limiting nutrient, input from various
origins can make a water system prone
to eutrophication, with impacts ranging
from the increased turbidity and floating
mats of macro algae shading out
beneficial submersed aquatic vegetation
habitat, to the exacerbation of noxious
algae blooms, to the creation of low or
no-oxygen conditions which negatively
affect fish populations. The National
Park Service (NPS) has reported that
loadings of total nitrogen deposition
(wet and dry) have caused changes in
aquatic chemistry and biota in the
Rocky Mountain National Park’s high
elevation ecosystems. (U.S. Department
of the Interior, 2002.) In the same report,
the NPS noted that increasing trends in
nitrogen deposition at many parks in the
western U.S. result from both nitrate
and ammonium.
The key to creating a linkage between
levels of nitrogen deposition and the
eutrophication of aquatic systems is to
demonstrate that the productivity of the
system is limited by nitrogen
availability, and to show that nitrogen
deposition is a major source of nitrogen
to the system. Thus, while it appears
that nitrogen inputs to aquatic systems
may be of general concern for eutrophic
conditions, the significance of nitrogen
input will vary from site to site. (1995
Staff Paper at 77.)
A 1993 National Research Council
report identifying eutrophication as the
most serious pollution problem facing
the estuarine waters of the U.S. was
reported in an EPA document issued in
1997, entitled ‘‘Nitrogen Oxides:
Impacts on Public Health and the
Environment’’ (p. 79). Nitrogen input is
a major concern because nitrogen is the
limiting nutrient for algae growth in
many estuaries and coastal water
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systems. In contrast to the
eutrophication concern, acidification
typically is not a concern, because
estuaries and coastal waters receive
substantial amount of weathered
material from terrestrial ecosystems and
from exchange with sea water.
Estimation of the contribution of
atmospheric nitrogen deposition to the
eutrophication problem can be difficult
because of the various direct
anthropogenic sources of nitrogen,
including agricultural runoff and
sewage. Some studies have shown that
nitrogen deposited from the atmosphere
can be a significant portion of the total
nitrogen loadings in specific locations,
such as the Chesapeake Bay—the largest
of the 130 estuaries in the U.S. It has
been estimated that the proportion of
the total nitrate load to the Bay
attributable to nitrogen deposition
ranges from 10 to 45 percent (NAPAP,
1998).
In most freshwater systems, including
lakes and streams, phosphorus, not
nitrogen, is the limiting nutrient. Thus,
eutrophication by nitrogen inputs will
only be a concern in lakes that are
chronically nitrogen limited and have a
substantial total phosphorus
concentration. This condition is
common only in lakes that have
received excessive inputs of
anthropogenic phosphorous, or in rare
cases, have high concentrations of
natural phosphorus. In the former case,
the primary dysfunction of the lakes is
an excess supply of phosphorus, and
controlling nitrogen deposition would
be an ineffective method of gaining
water quality improvement. In the latter
case, nitrogen deposition can
measurably increase biomass and thus
contribute to eutrophication in lakes
with high concentrations of natural
phosphorus. Other lakes, including
some high-elevation lakes in the Rocky
Mountains and Sierra Nevada, are very
low in both phosphorus and nitrogen;
addition of nitrogen can increase
biomass and contribute to
eutrophication in these lakes also.
(4) Visibility impairment (Regional
Haze). Nitrate particulates, formed as a
result of chemical reactions involving
NO and NO2 with other substances in
the atmosphere, are considered to be
more responsible for visibility
impairment than NO2 directly. Nitrate
particles are observed as both fine and
coarse particles. The fine particles that
can remain airborne for considerable
periods of time and may be transported
long distances from the NOX source.
These fine particles impair visibility by
scattering or absorbing light.
Generally, the two largest contributors
to visibility impairment are sulfates and
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carbon-based particles. The major cause
of visibility impairment in the East is
sulfate. Nitrates account for only 7 to 16
percent of the light extinction in the
East, but are responsible for between 4
and 45 percent of the light extinction in
the West. While NO2, a precursor of
nitrate particulates, is minimized
through the control of NOX emissions
from new and modified major stationary
sources under the PSD requirements for
NOX, EPA believes that the problems
associated with nitrate particulates,
along with other forms of PM, are best
addressed through programs focusing on
strategies to effectively reduce PM. For
example, EPA’s Regional Haze program,
established pursuant to section 169B of
the Act, specifically requires reductions
in NOX emissions from certain existing
stationary sources. The EPA also
recognized the significance of NOX
emissions as an important precursor of
PM2.5 under its June 2004 proposal for
CAIR. Accordingly, EPA proposed to
assign emission reduction requirements
to States that significantly contribute to
nonattainment in a downwind State
with respect to the PM2.5 NAAQS. Both
the Regional Haze program and the
proposed CAIR are discussed in greater
detail later in this preamble.
VI. Proposed Actions
As noted above, section 166 directs
EPA to conduct a study and promulgate
regulations to prevent significant
deterioration of air quality due to NOX
emissions. Those regulations may
include increments or ‘‘other measures’’
to prevent significant deterioration of air
quality, so long as those other measures
are consistent with the requirements of
sections 166(c) and 166(d) of the Act.
Accordingly, we are today proposing
three options for addressing the
statutory requirement for preventing
significant deterioration of air quality
due to emissions of NOX which we
believe satisfy the specific criteria
described herein. The first option
involves retaining the existing NO2
increments, and the other two options
qualify as ‘‘other measures’’ and include
using (1) a cap and trade program in lieu
of increments, and (2) a State planning
option providing States with some
flexibility for developing ‘‘other
measures’’ to adequately prevent
significant deterioration of air quality
due to emissions of NOX.
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A. Retain Existing Increment System for
NOX
1. How Existing Characteristics of the
Regulatory Scheme Fulfill Statutory
Criteria
As discussed above, EPA does not
interpret the Court’s decision to require
that EPA reevaluate the entire regulatory
framework of the PSD regulations for
NOX established in 1988. Thus, for the
increment system for NOX set forth in
this proposal, EPA is only reevaluating
the level, time period, and pollutant
form (NO2) used in establishing
increments in its PSD regulations for
NOX.
Because section 166 of the Act
requires that EPA establish PSD
regulations for NOX that satisfy the
criteria set forth in subsections (c) and
(d), EPA interprets section 166 to
require that its PSD regulations for a
particular pollutant must, as a whole,
satisfy the criteria in section 166.
However, in this unusual circumstance
where EPA is reevaluating specific
aspects of a larger body of PSD
regulations under an order of a court,
EPA does not necessarily consider all of
the criteria in section 166(c) of the Act
to be relevant to the specific issues
addressed by the court regarding the
characteristics of an increment. The
EPA believes that many of the factors
applicable under section 166(c) are
fulfilled by elements of the increment
and area classification regulatory
framework that were not controverted in
EDF v. EPA. Thus, EPA has not
conducted an extensive review of the
existing increments based on those
factors that are sufficiently satisfied by
the overall increment and area
classification system that was not
controverted.
However, we believe it is helpful to
explain how several aspects of the
overall system of regulations EPA
adopted for NOX under section 166
satisfy the factors applicable under
section 166(c). We believe our
obligations under section 166(c) of the
Act are satisfied when the entire body
of pollutant-specific PSD regulations for
NOX (including the level and other
characteristics of any increment) as a
whole meet the factors applicable under
166(c) of the Act.
a. Increment System
An increment is the maximum
allowable increase in air pollution that
is allowed to occur above baseline
concentrations. The baseline
concentration in a particular area is the
ambient pollutant concentration in an
area at the time the first complete PSD
permit application is submitted (i.e., the
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baseline date) by a new major stationary
source or a major modification for a
source affecting that area. By
establishing the maximum allowable
level of increase in air pollution in a
particular area, an increment defines
‘‘significant deterioration.’’ Once a
proposed new major stationary source
or major modification establishes the
baseline date in a particular area, the
new emissions from that source
consume increment in that area, as do
any subsequent emissions increases that
occur from any source in the area. When
the increment is totally consumed,
additional PSD permits cannot be issued
until sufficient amounts of the
increment are ‘‘freed up’’ via emissions
reductions that may be required by the
permitting authority. Moreover, the air
quality in a region cannot deteriorate to
a level in excess of the applicable
NAAQS, even if all the increment has
not been consumed. Thus, areas
experiencing air quality levels near the
level allowed by the NAAQS may not be
able to use the full amount of pollutant
concentration increase allowed by the
increment.
Congress did not require EPA to
utilize increments in its PSD regulations
for NOX promulgated under section 166
but gave EPA the discretion to employ
increments if appropriate to meet the
criteria and goals and purposes set forth
in sections 166 and 160. 42 U.S.C.
7474(d); EDF v. EPA, 898 F.2d at 185
(‘‘Congress contemplated that EPA
might use increments’’). In adopting its
PSD regulations for NOX in 1988, EPA
elected to base those regulations on the
concept of an increment because
increments represented the most
workable option at the time for
establishing a numerical measure
against which permit applications could
be evaluated. In addition, EPA
recognized that in using the increment
approach, it would be able to take
advantage of expertise that State and
local agencies had already developed in
implementing an increment-based
program for PM and SO2. 53 FR 40657.
Thus, EPA concluded that an
increment-based program was the best
way to fulfill its obligation under
section 166(c) to provide ‘‘specific
numerical measures against which
permit applications may be evaluated.’’
Under section 165(a)(3) of the Act, a
permit applicant must demonstrate that
emissions from the proposed
construction and operation of a facility
‘‘will not cause, or contribute to, air
pollution in excess of any (A) maximum
allowable increase or maximum
allowable concentration for any
pollutant.’’ 42 U.S.C. 7475(a)(3). An
increment is a quantitative value that
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establishes the ‘‘maximum allowable
increase’’ for a particular pollutant. It
functions, therefore, as a specific
numerical measure that can be used to
evaluate whether an applicant’s
proposed project will cause or
contribute to air pollution in excess of
allowable levels. Since this aspect of
EPA’s regulations was not controverted
in EDF v. EPA, we are not proposing to
revisit this criterion in our analysis of
the characteristics of the increments
below.
In addition, EPA also determined that
using increments in the PSD regulations
for NOX also satisfied the second factor
in section 166(c) by providing ‘‘a
framework for stimulating improved
control technology.’’ In 1988, we
concluded that increments establish an
incentive to apply more stringent
control technologies in order to avoid
violating the increment. 53 FR 40657.
Given that the PSD increment level is
consumed over time, the level of control
required to avoid causing exceedance of
the increment becomes more stringent.
Consequently, new or modified sources
in such localities may have to install
control technologies more effective than
those normally considered
representative of BACT in order to
comply with the increment, or to
preserve some portion of the increment
for future economic growth. The control
technologies utilized in these areas will
become the basis of BACT
determinations elsewhere, as the
technologies become more
commonplace and the costs tend to fall.
See also S. Rep. 95–127 at 18, 30 (3 LH
at 1392, 1404) (‘‘the incremental ceiling
should serve as an incentive to
technology, as a potential source may
wish to push the frontiers of technology
in a particular case to obtain greater
productive capacity within the limits of
the increments’’). We believe the
existing regulatory framework, which
was not controverted in EPA v. EDF,
satisfies this criterion and do not
propose to reconsider it under the
increment option of this proposal.
b. Area Classifications
In 1988, EPA chose to establish NO2
increments of different stringency based
on the three-tiered classification scheme
established by Congress. 53 FR 40657.
Under this scheme, Class I areas are
generally national parks, wilderness
areas, and other special areas that
require an extra level of protection. The
most stringent increment is imposed in
Class I areas. Class III areas, which have
the least stringent increment level, are
those areas in where a State wishes to
permit a higher level of industrial
development. Areas that are not
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especially sensitive or that do not wish
to allow for a higher level of industrial
growth are classified as Class II. When
Congress established this three-tiered
scheme for SO2 and PM, it intended that
Class II areas be subject to an increment
that allows ‘‘moderately large increases
over existing pollution.’’ H.R. Rep. 95–
294, 4 Legislative History at 2609. The
Petitioner’s in EDF v. EPA did not
contest EPA’s decision to employ this
same classification scheme for NOX. We
believe that adopting such an area
classification scheme for NOX with a
different level of increment for each
type of area helps to fulfill two of the
factors applicable under section 166(c)
of the Act.
First, Class I areas generally cover the
kinds of parks and special areas covered
by section 160(2) of the Act. Thus,
establishing the lowest level of
increment in these areas helps fulfill
EPA’s obligation to establish regulations
for NOX that ‘‘preserve, protect, and
enhance the air quality’’ in these areas.
With the air quality in Class I areas
subject to the greatest protection, this
scheme then provides two additional
area classifications with higher
increment levels to help satisfy the goal
in section 160(3) of the Act that EPA
‘‘insure that economic growth will occur
in a manner consistent with
preservation of clean air resources.’’ In
those areas where clean air resources
may not require as much protection,
more growth is allowed. By employing
an intermediate level (Class II areas) and
higher level (Class III areas), this
classification scheme helps ensure that
growth can occur where it is needed
(Class III areas) without putting as much
pressure on existing clean air resources
in other areas where some growth is still
desired (Class II areas).
By redesignating an existing Class II
area to Class III, States may
accommodate economic growth and air
quality in areas where the Class II
increment is too stringent to allow the
siting of new or modified sources. The
procedures specified by the Act for such
a redesignation require a commitment of
the State government to the creation of
such an area, extensive public review,
participation in the State
Implementations Plan (SIP) area
redesignation process, and a finding that
the redesignation will not result in the
applicable increment being exceeded in
a nearby Class I or Class II area. See 42
U.S.C. 7474(a)–(b) (Section 164(a)–(b)).
Our 1988 analysis, 53 FR at 3702–05
and the subsequent issuance of PSD
permits for major new and modified
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sources of NOX since that time,20 tend
to confirm that, with the existing
increment levels, the three-tiered
classification system has allowed for
economic growth, consistent with the
preservation of clean air resources.
Because it helps fulfill these goals and
purposes and was not controverted in
EDF v. EPA, we do not propose to revisit
our decision to employ this area
classification scheme for NOX. However,
we do not believe that this framework
alone completely satisfies the factors
applicable under section 166(c) of the
Act. The increment level that is
employed for each class of area is also
relevant to an evaluation of whether the
area classification scheme achieves the
competing goals of the PSD program.
Thus, we propose to further consider
the goals of protecting parks and special
areas and ensuring economic growth
consistent with the preservation of clean
air resources as we reevaluate the
increment levels at the direction of the
Court.
c. Permitting Procedures
The framework of our existing PSD
regulations employs the preconstruction
permitting system and procedures
required under section 165 of the Act.
42 U.S.C. 7475. These requirements are
generally reflected in sections 51.166
and 52.21 of EPA’s PSD regulations in
Title 40 of the Code of Federal
Regulations. These permitting and
review procedures, which we interpret
to apply to construction on any new or
modified major source, fulfill several of
the factors applicable under section
166(c) of the Act for EPA’s PSD
regulations for NOX. Two of the goals
and purposes of the PSD program, in
particular, seem especially amenable to
being fulfilled through a case-by-base
permit review.
Under section 160(5) of the Act, as
incorporated in section 166(c), EPA
should develop PSD regulations for NOX
that ‘‘assure that any decision to permit
increased air pollution in any area to
which this part applies is made only
after careful evaluation of all the
consequences of such a decision, and
after adequate procedural opportunities
for informed public participation in the
decisionmaking process.’’ The permit
evaluation and review procedures
reflected in the existing PSD
regulations, which are applicable to
sources of NOX, call for a careful
evaluation that involves a source impact
analysis (sections 51.166(k) and
20 EPA does not formally track the issuance of
PSD permits across the country, but EPA’s Regional
Offices have confirmed that various PSD permits for
sources of NOX have been issued by many of the
States in their respective jurisdictions.
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52.21(k)), air quality analysis (sections
51.166(m) and 52.21(m)), additional
impacts analysis (sections 51.166(o) and
52.21(o)), and an analysis of impacts on
Class I areas (sections 51.166(p) and
52.21(p)). In addition, the procedures
incorporated in sections 51.166(q) and
52.21(q) ensure public participation in
the decisionmaking process. Thus, we
believe the existing framework for the
PSD regulations for NOX fulfills the
goals and purposes set forth in section
160(5) by employing the permit review
procedures described above. Because
the goal in section 160(5) is satisfied by
the existing regulatory framework that
was not controverted in EDF v. EPA, we
do not propose to further consider this
factor in our evaluation of the
characteristics of the NO2 increment.
In addition, we believe the permit
review component of the framework
also fulfills the goals and purposes set
forth in section 160(4) of the Act. As
incorporated through section 166(c) of
the Act, section 160(4) calls on EPA to
establish PSD regulations that prevent
one State from interfering with the PSD
program for any other State. This goal is
also one that we believe can be best
implemented through individual permit
review when we use an increment
system. In the course of such a review,
a source must demonstrate that it does
not cause or contribute to an increment
violation in any area subject to part C
of the Act. See section 165(a)(3)(A).
These areas include areas in other
States. Thus, we do not propose to
further consider the goal in section
160(4) in our reevaluation of the
characteristics of the NO2 increments.
We believe the existing permit
evaluation procedures incorporated into
the framework of our existing PSD
regulations for NOX operate to satisfy
the goal in section 160(4) and do not
require further analysis for the
increment option.
d. Additional Impacts Analysis
One particular aspect of the permit
review procedures described above is
worthy of more particular attention
because it also helps fulfill the
substantive criteria and goals and
purposes in section 166(c) and section
160. Where applicable, the additional
impact analysis required under section
165(e)(3)(B) and the PSD regulations
(§§ 51.166(o), 52.21(o)) provides a caseby-case review of the potential harm
that a pollutant may cause to certain
resources in all classes of areas. The
following type of analysis is required to
be conducted by the permit applicant:
(1) The owner or operator shall provide an
analysis of the impairment to visibility, soils
and vegetation that would occur as a result
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of the source or modification, and general
commercial, residential, industrial and other
growth associated with the source or
modification. The owner or operator need not
provide an analysis of the impact on
vegetation having no significant commercial
or recreational value.
(2) The owner or operator shall provide an
analysis of the air quality impact projected
for the area as a result of general commercial,
residential, industrial, and other growth
associated with the source or modification.
Section 165(e)(3)(B). The Additional
Impacts Analysis requirements are the
most relevant in this rulemaking action
to Class II and Class III areas which are
not subject to the additional FLM
review that applies in Class I areas.
e. Federal Land Manager Review
In the 1988 rulemaking addressing
PSD for NOX, EPA extended the FLM
review procedures set forth in sections
51.166(p) and 52.21(p) to cover NO2. 53
FR at 3704. These FLM review
procedures were established based on
section 165(d), and they were originally
applied only in the context of the
statutory increments for PM and SO2.
However, because they also address
many of the factors applicable under
section 166(c) of the Act, EPA also
applied them to NOX through
regulation. Under an increment
approach, we view the FLM review
procedures as an additional measure
that helps to satisfy the factors in
sections 166(c) and 160(2) which
require that EPA’s PSD regulations for
NOX protect air quality values and parks
and other special areas.
Section 165(d) creates a scheme under
which the FLM has an affirmative
responsibility to protect the AQRVs in
Class I areas, and may object to or
concur in the issuance of a PSD permit
based on the impact or lack thereof on
any affected AQRV that the FLM has
identified, irrespective of whether the
increment is exceeded. The exceedance
of the increment determines only where
the burden of proof lies.21
That is, if the proposed source will
cause or contribute to a violation of a
Class I increment, the permitting
authority (State or EPA) shall not issue
the permit unless the owner or operator
demonstrates to the satisfaction of the
FLM that there will be no adverse
impact on AQRVs.22 On the other hand,
21 In response to concerns that Class I increment
would hinder growth in areas surrounding the Class
I area, Class I increments were established as a
means of determining where the burden of proof
should lie for a demonstration of adverse effects on
AQRVs. See Senate Debate, June 8, 1977 (3 LH at
725).
22 Even if such a waiver of the Class I increment
is allowed upon a finding of no adverse impact, the
source must comply with such emissions
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if the proposed source does not cause or
contribute to a violation of a Class I
increment, the FLM may only prevent
issuance of the permit by demonstrating
to the satisfaction of the permitting
authority that the source will have an
adverse impact on AQRVs. Section
165(d)(2)(C).
Incorporating these FLM procedures
into the PSD regulations for NOX helps
to provide protection for parks and
special areas (which are generally the
Class I areas subject to this review) and
air quality values (which are factors
considered in the review). Section
166(d) on its face provides that
measures other than increments may be
promulgated to satisfy the duty under
section 166.
Legislative history indicates that the
FLM provisions of section 165(d) were
intended to provide another layer of
protection, beyond that provided by
increments. The Senate committee
report stated the following: ‘‘A second
test of protection is provided in
specified Federal land areas (Class I
areas), such as national parks and
wilderness areas; these areas are also
subjected to a review process based on
the effect of pollution on the area’s air
quality related values.’’ S. Rep. 95–127,
at 17, 4 Legislative History at 1401.
f. Installation of Best Available Control
Technology
Finally, another important element of
the existing framework of PSD
regulations applicable to NOX emissions
is the requirement that a permit
applicant apply BACT when
constructing a new source or making a
major modification to an existing
source. This requirement, based on
section 165(a)(4) of the CAA, is
included in EPA’s PSD regulations and
thus is also part of the regulatory
framework for the Agency’s pollutantspecific regulations for NOX. 40 CFR
52.21(j); 40 CFR 51.166(j). Our existing
regulations define ‘‘best available
control technology’’ as ‘‘an emission
limitation * * * based on the maximum
degree of reduction for each pollutant
subject to regulation under the Act
* * * which the Administrator, on a
case-by-case basis, taking into account
energy, environmental, and economic
impacts and other costs, determines is
achievable for such source through
application of production processes or
available methods, systems, and
limitations as may be necessary to ensure that the
Class II increment for SO2 or PM is not exceeded.
Section 165(d)(2)(C)(iv). In 1988, EPA made this
provision applicable to the PSD provisions for NOX,
with a cap of 25 µg/m3 · the NO2 Class II
increment. 53 FR at 3704; 40 CFR 51.166(p)(4) and
52.21(p)(5).
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8897
techniques * * *.’’ 40 CFR 52.21(b)(12);
40 CFR 52.166(b)(12). This pollutant
control technology requirement is
rigorous and in practice has required
significant reductions in the pollutant
emissions from new and modified
sources. Thus, the BACT requirement is
an additional measure in the framework
of PSD regulations for NOX that helps to
satisfy the factors in sections 166(c),
160(1), and 160(2), which require that
EPA’s PSD regulations for NOX protect
air quality values, public health and
welfare, and parks and other special
areas.
2. Proposed Actions Regarding
Characteristics of NO2 Increments
We believe our review of the
characteristics of the existing NO2
increments should apply the following
four factors applicable under section
166(c): (1) Protect air quality values; (2)
protect public health and welfare from
adverse effects from air pollution that
occur even if in attainment; (3) protect
air quality in parks and special areas;
and (4) ensure economic growth
consistent with preservation of clean air
resources.23 As noted earlier, we believe
sections 166 and 160 direct that we
balance the fourth factor (fostering
economic growth) against the other
three environmentally protective factors
listed above. The other four factors
identified in sections 166(c) and 160 of
the Act do not appear to relate to the
characteristics of the increments and are
more appropriately considered when
establishing the overall framework for
PSD regulations. As described above, we
believe that the framework adopted for
the PSD regulations for NOX satisfies the
other factors. Since EPA is not
reconsidering the entire framework in
this proposed option, we do not believe
that it is appropriate to further consider
these other four factors.
a. Level of Increment
Consistent with the ‘‘contingent safe
harbor’’ approach described above, our
analysis of the appropriate levels for
NO2 increments begins by establishing a
‘‘safe harbor’’ increment level that is ‘‘at
least as effective as’’ the increments
established by Congress in section 163
of Act. 42 U.S.C. 7476(d). The court in
EDF v. EPA recognized that this
standard from section 166(d) of the Act
is satisfied when we establish
increments using the percentage-ofNAAQS approach that Congress used to
establish the statutory increments. See
23 We paraphrase these factors here and in the
sections that follow to facilitate the explanation of
our reasoning. However, we recognize that the
statutory language is broader than the shorthand we
use here for convenience.
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898 F.2d at 188. This approach involves
using the same percentages that
Congress used to calculate the PM and
SO2 increments from the NAAQS in
effect at that time for these pollutants.
Because the only oxide of nitrogen for
which we have a NAAQS is NO2, we
can only utilize the percentage of
NAAQS approach to establish a ‘‘safe
harbor’’ increment level for NO2. We
consider below whether we should
establish increments for other forms of
NOX.
Because Congress used different
percentages to calculate the Class I
increments for PM and SO2, we must
determine which of these percentages is
appropriate for the Class I NO2
increment. For the reasons described in
the 1988 rulemaking, we believe that it
is appropriate for NO2 increments to be
derived using the same percentages that
Congress used for SO2 because NO2
more closely resembles SO2 than PM in
its characteristics and sources. See 53
FR 3698, 3700 (February 8, 1988). Thus,
we begin our analysis with a ‘‘safe
harbor’’ increment level for each class of
area that is set at the same percentage
of the NO2 NAAQS as the SO2
increment is of the SO2 NAAQS.
Because the NO2 increments have not
changed since 1988, the percentage-ofNAAQS approach yields the same levels
that we derived in 1988. Thus, using
this approach, the ‘‘safe harbor’’ level
for the Class I increment for NO2 is 2.5
µg/m3 (annual average), a level that is
2.5 percent of the NO2 NAAQS. For the
Class II increment for NO2, the ‘‘safe
harbor’’ level is 25 µg/m3 · 25 percent
of the NO2 NAAQS. For the Class III
increment for NO2, the ‘‘safe harbor’’
level is 50 µg/m3 · 50 percent of the
NO2 NAAQS.
Under our interpretation of the Act,
these ‘‘safe harbor’’ levels establish the
minimum stringency levels (or highest
concentration levels) that we may use as
the increments for NO2. Our next step
is to consider the factors applicable
under section 166(c) and evaluate
whether we need to revise the ‘‘safe
harbor’’ level to satisfy these factors.
Thus, under the increment option in
this proposed rulemaking, to satisfy the
requirements of section 166 of the Act,
we believe we must evaluate whether it
is necessary to adjust the NO2
increments to levels more stringent than
the ‘‘safe harbor’’ levels we derived
using the percentage-of-NAAQSapproach. In this analysis of the level of
each increment, we propose to apply the
four factors applicable under section
166(c) that have not already been
satisfied by the regulatory framework
described above. Thus, we consider
whether different increment levels are
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necessary to (1) protect air quality
values; (2) protect public health and
welfare from any effects occurring at
levels below the NAAQS; (3) protect
parks and special areas; and (4) ensure
economic growth consistent with
preservation of clean air resources.
(1) An increment is an allowable
marginal increase in air pollution.
Increments represent the maximum
allowable level of increase in an area
that is in attainment with the NAAQS
or unclassifiable. Thus, increments are
essentially a marginal level of increase
in air pollution that is allowable for
particular areas. The statutory
increments are expressed as
concentration rather than mass values.
Thus, in applying the factors applicable
under section 166(c), we believe section
166 of the Act requires that we analyze
the impacts on air quality values, health
and welfare, and parks and special areas
that may occur as a result of some
marginal increase in the concentration
of air pollution in an area.
Using the ‘‘contingent safe harbor’’
approach, we first derive the highest
level of marginal increase that may be
permitted for each class of areas using
the percentage-of-the-NAAQS approach.
We must then consider whether this
level of marginal increase satisfies the
factors applicable under section 166(c).
If the marginal increase in concentration
allowed by the ‘‘safe harbor’’ level does
not adequately protect against these
effects and ensure economic growth
consistent with preservation of clean air
resources, then we must attempt to
identify an alternative level of marginal
increase that will satisfy the factors
applicable under section 166(c).
As noted earlier, EPA does not
interpret the PSD program to require it
to set increments at a level where there
will be no adverse effects from a
marginal increase in air pollution in the
amount of the increment. Congress did
not anticipate that an increment would
be a level of increase below which there
would be no effects. An increment is the
level that defines ‘‘significant’’
deterioration but does not prohibit all
deterioration of air quality. The PSD
program allows for some increase in
effects when necessary to ensure that
economic growth may continue to occur
consistent with the preservation of clean
air resources.
(2) Increments are not intended to
remedy existing effects but to maintain
levels of air quality achieved by other
programs. Because an increment is an
allowable level of increase, it does not
function to reduce existing air pollution.
The PSD program is intended to protect
against significant deterioration of the
air quality in attainment and
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unclassifiable areas from the
construction and operation of new and
modified sources of a particular size.
Thus, the PSD program limits increases
in emissions from these sources but
does not seek to reduce emissions or
ambient air pollutant concentrations to
a particular level. The increments
established by Congress were only
intended to define the allowable levels
of marginal increase in air pollution
above a baseline concentration that are
established in each area when the first
major source applies for a PSD permit
in that area. 42 U.S.C. 7479(4). As a
result, we do not believe we are
required to set increments at a level
intended to alleviate existing adverse
effects.
An increment is a marginal level of
increase in air pollutant concentrations
that functions to prevent significant
deterioration of air quality. Thus, in
evaluating the increment levels that are
necessary to prevent significant
deterioration of air quality, we consider
that there are other programs authorized
under the CAA that are operating (or
will be operating) to reduce the adverse
effects from existing air pollution
sources. If we use an increment
approach, these programs will serve the
role of bringing existing emissions
down, while increments included in our
PSD regulations established under
section 166 of the Act will be designed
to limit increases in emissions from the
construction of new major sources and
the modification of existing ones.
For example, existing visibility
problems are being addressed through
implementation of the Regional Haze
Program under sections 169A and 169B
of part C.24 Section 169A establishes as
a national goal ‘‘the prevention of any
future, and the remedying of any
existing, impairment of visibility in
mandatory Class I Federal areas which
impairment results from manmade
pollution.’’ 42 U.S.C. 7491(a). In the
1990 Amendments, Congress added
section 169B, which called for
additional research into the visibility
problem and directed EPA to issue
regional haze rules taking into account
such studies and reports within 18
24 When the visibility provisions were enacted,
the House committee report specifically recognized
that the ‘‘visibility problem is caused primarily by
emission into the atmosphere of sulfur dioxide,
oxides of nitrogen, and particulate matter * * *’’
H.R. Rep. 95–294, at 204, reprinted in 4 Legislative
History at 2671. NOX may result in visibility
impairment either locally (a brown plume effect) or
contributing to regional haze, which has been
recognized as primarily a fine particle
phenomenon. 1995 Staff Paper at 89. For the
reasons discussed earlier, we do not believe we
need to consider PM effects in this reevaluation of
the NO2 increments.
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months after receipt of a final report
from the Grand Canyon Transport
Visibility Commission. The EPA
promulgated these regulations on July 1,
1999. 64 FR 35714 (‘‘Regional Haze
rule’’). The main components of this
rule require States to: (1) Submit SIPs
that provide for ‘‘reasonable progress’’
toward achieving ‘‘natural visibility
conditions’’ in Class I areas; (2) provide
for an improvement in visibility in the
20 percent most impaired days; (3)
ensure no degradation in visibility
occurs on the 20 percent clearest days;
and (4) determine the annual rate of
visibility improvement that would lead
to ‘‘natural visibility’’ conditions in 60
years.
At the time that the Regional Haze
Program was established, a
Congressional committee recognized
that the PSD program was not
necessarily created to alleviate existing
adverse effects resulting from
contributions by existing sources. When
it was writing section 169A of the Act
at the same time that it established the
PSD program, the House recorded the
following observations in a committee
report:
[T]he committee recognizes that one
mechanism which has been suggested for
protecting these areas, the mandatory Class I
increments of new section 160 (‘Prevention
of Significant Deterioration’) do not protect
adequately visibility in Class I areas. First,
inadequately controlled, existing gross
emitters such as the Four Corners plant
would not be affected by the significant
deterioration provisions of the bill. Their
emissions are part of the baseline, and would
not be required to be reduced by new section
160 of the act.
H. Rep. 95–294, at 205, 4 Legis. History
at 2672 (emphasis added). This
statement indicates that protection of air
quality values under section 166(c) is
provided when an increment limits
significant deterioration of air quality,
but does not require an increment that
eliminates all adverse impacts on air
quality values, such as visibility, that
may be caused by existing sources.
In addition, in the 1990 Amendments,
Congress enacted title IV to address the
problem of acid deposition. We believe
this supports an interpretation that the
PSD measures called for in section 166
need not eliminate acid deposition
impacts that may be caused by existing
sources. Rather, under an increment
approach, our view is that the PSD
program is intended to focus on
establishing a marginal level of increase
in emissions that will prevent
significant air quality deterioration and,
in conjunction with AQRVs identified
by the FLM, provide protection against
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increases in adverse effects resulting
from acid deposition.
Reduction of NOX emissions from
existing sources is also required under
EPA’s NOX SIP Call and the proposed
CAIR. Under both programs, emissions
of NOX are regulated as a precursor of
either ozone or fine PM, or both. The
programs are based on State obligations
to address interstate transport of
pollution under section 110(a)(2)(D) of
the Act, which is discussed in more
detail above in the section on our legal
authority.
The NOX SIP Call requires the
affected States and the District of
Columbia to submit SIP revisions that
reduce NOX emissions by specified
amounts by a specified date. The EPA
has projected that over 1 million tons of
NOX per ozone season will be reduced
as a result of this particular program.
As proposed, the CAIR requires that
emissions reductions be implemented in
two phases, with the first phase in 2010
and the second phase in 2015. The
EPA’s estimates of the NOX emissions
reductions that would result from the
CAIR proposal are 1.5 million tons by
2010 and an additional 0.3 million tons
by 2015 (for a total of 1.8 million tons).
In areas where the PSD baseline has
not yet been established, the emissions
reductions achieved by these programs
may result in lower baselines being
established when triggering does occur.
Then, the increments we are
reevaluating in this rulemaking will
begin to operate as an allowable level of
marginal increase that prevents the
significant deterioration of air quality in
attainment areas. This approach is
consistent with Congressional intent
that the baseline concentration,
representing the air quality in an
attainment area subject to PSD, be
established on the date of the first
application for a permit by a PSD source
affecting that area. 42 U.S.C. 7479(4).
See also, Alabama Power v. Castle, 606
F.2d 1068, 1088–89 (D.C. Cir. 1979).
(3) Increments should be uniform
across the nation. When we use the
framework of an area classification
system in PSD regulations for a
particular pollutant, we believe that we
must establish a single increment for
each class of area such that this
allowable level of increase applies
uniformly to all areas in the nation with
that particular classification. This is
necessary to ensure equitable treatment
by allowing the same level of economic
growth for all regions of the country that
a State elects to classify in a particular
manner. We believe that Congress
intended for the PSD program to allow
air quality in each area of the country
with the same classification to change
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8899
by the same amount in order to avoid
a disproportionate impact on growth
that might disadvantage some
communities. The following statement
from the legislative history of the PSD
program supports our interpretation:
Some suggestions were made that the
pollution increments should be calculated as
a function of existing levels of pollution in
each area. But the inequities inherent in such
an approach are readily evident * * *. The
committee’s approach—increments
calculated as a percentage of the national
standard—eliminates those inequities. All
areas of the same classification would be
allowed the same absolute increase in
pollution, regardless of existing levels of
pollution.
H. Rep. 95–294, at 153, 4 Legis. History
at 2620. See also S. Rep. 95–127, at 30,
3 Legislative History at 1404 (‘‘These
increments are the same for all
nondeterioration areas, thus providing
equity for all areas.’’). This indicates
that Congress did not intend to impose
more stringent restrictions under the
PSD program on particular areas of the
country based on their current levels of
air pollution, unless, of course, the
current levels are so near the NAAQS
that the full amount of incremental
change cannot be allowed.
Instead, Congress generally left it up
to the States to determine the areas
where a greater or lesser level of
protection was needed. Although
Congress established certain parks and
wilderness areas as mandatory Class I
areas, it classified all other areas as
Class II areas and gave the States the
power to reclassify these areas to Class
I or Class III to provide for greater
protection of air quality or allow more
growth, depending on the values of the
State and the community in that area.
This allows the States to make their own
choices about which areas require more
protection of air quality and which areas
should be allowed more growth
consistent with the protection of air
quality. See H.R. Rep. 95–294, at 153–
154, 4 Legislative History at 2620–2621.
We believe that the same equitable
considerations are applicable when we
establish PSD regulations containing
increments and area classifications
under section 166 of the Act. Since
Congress did not intend for the
increments it established to impose a
disproportionate impact on particular
areas, we do not believe it intended to
grant EPA the power to do so under
section 166 of the Act. Thus, to treat all
areas of the country in an equitable
manner, it is necessary for us to
establish uniform increments for NO2
that establish the same maximum
allowable increase for each class of area.
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However, we must also weigh these
equitable considerations against the
unique variability in ecosystem effects
that may result from NOX emissions. In
our review of the NO2 NAAQS, we
observed that ‘‘a great degree of
diversity exists among ecosystem types,
as well as in the mechanism by which
these systems assimilate nitrogen
inputs.’’ 60 FR at 52881. As a result, we
concluded, ‘‘the relationship between
nitrogen deposition rates and their
potential environmental impact is to a
large degree site or regionally-specific
and may vary considerably over broader
geographical areas or from one system to
another because of the amount, form,
and timing of nitrogen deposition, forest
type and status, soil types and status,
the character of the receiving
waterbodies, the history of land
management and disturbances across
the watersheds and regions, and
exposure to other pollutants.’’ Id.
Consistent with these earlier
conclusions, our more recent review in
this rulemaking action of the studies on
the effects of NOX indicates that some
levels of air pollution resulting from
emissions of NOX may contribute to
adverse effects on welfare, air quality
values, and parks in some areas of the
country while not necessarily causing
the same degree of effects on similar
ecosystems and receptors in other areas
of the country.
In light of the equitable
considerations discussed earlier, we
believe the best way to address the
potential regional variability in the
occurrence of effects attributable to NOX
emissions is to retain uniform national
increments that accommodate growth
and provide a basic degree of protection
across the country, but to augment this
with a procedural review that will
require permitting authorities to
consider adverse effects that may occur
in more sensitive areas before the
increment is consumed. This approach,
which we believe is reflected in existing
regulations, allows EPA to achieve the
equity of setting a uniform increment
level for all areas with a particular
classification, while directing that
permitting authorities conduct a more
intensive, site-specific review to
identify effects that might occur in a
more sensitive area but not necessarily
in all areas of the country with that
classification.
This approach is embodied in the
framework for the PSD regulations for
NOX that we adopted in 1988. As
described above, each permit
application is subject to an ‘‘additional
impacts’’ analysis that allows the
permitting authority to consider the
sensitivity of a particular area. In Class
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I areas, the FLM review procedures
provide further protection,
notwithstanding the existence of a Class
I increment, for the air quality values
and the national parks and wilderness
areas included in Class I areas.
As we noted earlier, we believe our
ultimate obligation under section 166 of
the Act is to establish a system of
regulations containing provisions that
collectively satisfy the content
requirements in sections 166(c) and
166(d) of the Act. Thus, we think that
Congress contemplated that we would
consider the entire group of regulations
when establishing particular aspects of
those regulations. As a result, we
believe it is appropriate and consistent
with our statutory obligations to
consider the protection provided by the
additional impacts analysis and the
FLM review of AQRVs when evaluating
the level of NO2 increments. Therefore,
to achieve equity and protect against
effects that are variable across regions of
the country, we believe each of the NO2
increments should be set at a level that
reasonably protects air quality values,
health and welfare, and parks and
special areas across the country while
also balancing the need to allow
economic growth. To the extent
necessary, the case-by-case additional
impact analysis and FLM review should
provide additional protection of air
quality in particular areas that may be
more sensitive to nitrogen loadings
resulting from NOX emissions.
Because of the equitable
considerations and State prerogatives to
classify areas described above, we do
not believe that Congress intended to
create a federally imposed system of
regional or locally based measures or to
authorize EPA to do so to address any
variability in potential effects. Likewise,
we do not believe it is permissible or
appropriate for us to establish
increments at a level that prevents any
adverse impact on the most sensitive
receptors in any part of the country.
Although such a ‘‘lowest common
denominator’’ approach might achieve
uniformity across all areas, it would
unduly restrict growth in those areas of
the country where adverse effects may
not occur at a higher level. In addition,
as discussed further below, the available
research on the effects of NOX does not
readily provide sufficient information to
identify that level of increase below
which significant effects would not
occur to the most sensitive receptors in
any area of the country.
Thus, EPA believes that the factors
applicable under section 166(c) of the
Act are met when we establish a
uniform national increment for NO2 for
each class of area that is augmented by
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an additional case-by-case procedural
review to identify and protect against
variable effects that could occur in
especially sensitive areas before the
increment is fully consumed.
(4) Evaluation of effects at levels of
increase below the ‘‘safe harbor’’ level.
With the above considerations in mind,
we have reviewed the available effects
information to determine whether there
is a basis for using it to either support
the existing increments or to find them
inadequate for satisfying the criteria,
goals, and purposes set forth in sections
166(c) and 160 of the Act. Selecting a
framework for applying the criteria is an
important first step. Because the
increments define an allowable change
in air quality rather than establish a
uniform air quality ‘‘ceiling’’ for a
particular pollutant, we believe that the
basis for determining the adequacy of
the increments should be a comparison
of the maximum allowable pollutant
increase or change (ambient pollutant
concentration that would result from
full increment consumption) with the
pollutant concentrations at which the
effects of concern (particularly the
adverse effects associated with air
quality values under section 166(c) of
the Act) may occur. This approach relies
upon the premise that in specific
attainment areas where adverse effects
caused by existing emissions may be
experienced, specific control strategies
designed to adequately reduce current
levels of emissions (and air pollution)
will be evaluated and the most
appropriate course of action determined
independently from the PSD program.
The problem that EPA immediately
faces in trying to make the necessary
comparative analysis of the ‘‘safe
harbor’’ levels with lower increment
levels is that for the adverse effects
identified, in most instances the
pollutant concentrations at which the
effects may occur are not well defined.
Based on the availability of scientific
and technical information available
during the period when the NO2
increments were promulgated in 1988 as
well as for the periodic review of the
NO2 NAAQS completed in 1996, there
is great uncertainty about the specific
relationship between the pollutant and
its precise role in causing the effect.
Moreover, while more recent research
and studies have shed new light on the
mechanisms by which NO2
contributes—both directly and
indirectly—to known adverse
environmental effects, efforts to
establish quantitative relationships (as
explained further below) are only now
under way. Nevertheless, what is
already known about some of these
cause-effect relationships is also helpful
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in enabling us to reach a conclusion
about the adequacy of the current
increment levels.
As described earlier in the preamble
under the discussion of environmental
effects, many of the adverse effects
indirectly related to emissions of NOX
(NO and NO2) are caused (or
contributed to) largely by nitrogen
compounds (e.g., nitrates, nitric acid)
which are the result of chemical
transformations from NO2 while in the
atmosphere. Thus, in order to attempt to
determine an acceptable level of
increase for ambient NO2
concentrations, it is necessary to
understand the quantitative relationship
between the emissions of NO2 and the
adverse effect. This, in part, requires an
understanding of the intermediate
transformation processes, the deposition
patterns and total quantities of those
nitrogen compounds which may cause
the effect of concern, as well as the
nitrogen contribution to ecosystems
from natural geobiochemical processes.
Unfortunately, the atmospheric
chemistry associated with NOX is
significantly more complex than that for
SO2. In addition to wet and dry nitric
acid and nitrate aerosols such as
ammonium nitrate (NH4NO3), emissions
of NOX can also produce other end
products, such as peroxyacetyl nitrates
(PAN). Also, NOX may result, either
directly or indirectly, in the formation
of oxidant species such as the OH
radical, O3, and H2O2, which alter
transformation rates of NOX. (Butler,
2003.)
The difficulty of establishing these
relationships is further illustrated by
EPA’s experience in evaluating the
feasibility of setting an acid deposition
standard. Under section 404 of the 1990
Amendments, Public Law 101–549,
Congress directed EPA to conduct a
study of the feasibility and effectiveness
of an acid deposition standard(s), to
report to Congress on the role that a
deposition standard(s) might play in
supplementing the acidic deposition
program adopted in title IV, and to
determine what measures would be
needed to integrate an acid deposition
standard with that program. The EPA
completed this study, ‘‘Acid Deposition
Feasibility Study, Report to Congress’’
(1995), which concluded that current
scientific uncertainties associated with
determining the level of an acid
deposition standard(s) are significant,
and did not recommend setting an acid
deposition standard. See State of New
York v. Browner, 50 F. Supp. 2d 141,
149 (N.D.N.Y. 1999) (rejecting States’
claim that section 404 required that the
report include a deposition standard
that would be sufficient to protect
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sensitive aquatic and terrestrial
resources, and affirming EPA
interpretation that duty was limited to
‘‘consideration of a description’’ of such
standards). While EPA has recognized
that programs, such as the proposed
CAIR (69 FR 4566, Jan. 30, 2004)), that
are intended to achieve NOX emissions
reductions pursuant to other statutory
provisions, will help mitigate acid
deposition problems, none of those
programs purport to set an acid
deposition standard.
Some recent studies are attempting to
address the various parameters that
together could establish a quantitative
relationship between emissions of NOX
and the adverse environmental effects
resulting from nitrogen deposition and
acidic deposition from nitrates. While
some study results provide evidence of
a relationship between NOX emissions
and precipitation (wet deposition)
NO3·, the results of efforts to establish
a quantitative relationship between NOX
emissions and total (wet and dry)
nitrogen deposition have been
inconclusive (Butler, 2000, 2003).
Other recent studies examine the
various sources of the nitrogen input
(industry, transportation, agriculture)
the geographical location of different
nitrogen loadings, trends in deposition
rates, as well as the specific effects of
nitrogen deposition on specific
ecosystems. These studies in general
emphasize the importance of reducing
current emissions of NOX as part of a
strategy for reducing observed impacts
and promoting ecosystem recovery.
However, such studies have not yielded
the type of information needed to
adequately evaluate different levels of
maximum allowable pollutant increases
with respect to the specific impacts
such levels would have on the
ecosystems.
We have evaluated whether the
concept of a ‘‘critical load,’’ as described
more fully in section VII of this
preamble, could be used to identify an
alternative increment level, but we
believe our current knowledge about
critical loads for nitrogen does not
provide a sufficient basis for
establishing a uniform, national
standard such as a PSD increment.
Because of the vastly differing
sensitivities and potential effects
associated with ecosystem resources in
different regions of the country, we
believe that critical loads do not
represent an appropriate tool for setting
a single, uniform, national standard,
such as a PSD increment level. Even in
cases where the deposition rate of a
pollutant is relatively consistent from
one location to another, the sensitivity
of individual ecosystems varies greatly
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8901
depending on a number of different
variables, including climate, diversity of
species, history of land use, and the
existence of other natural and
anthropogenic stresses.
Identifying the cause-effect
relationship of nitrogen deposition on
various ecosystems can be problematic
for a number of other reasons as well.
Some effects are believed to be the
result of combined pollutant impacts,
such as the acidification of lakes from
both sulfur and nitrogen deposition.
Some water systems have exhibited high
levels of nitrogen in the absence of
anthropogenic sources. In addition,
some effects of changing deposition may
take years before the ecosystem comes
into balance with the cumulative
amounts of nitrogen inputs. A noted
problem in the West is that nitrogen
deposition can include the combined
contributions of emissions from NOX
(which form nitrates and nitric acid in
the atmosphere) and ammonia
(ammonium). Finally, current levels of
nitrogen deposition may provide
passive fertilization for forests and
terrestrial ecosystems where nutrients
are a limiting factor and for some
croplands.
As discussed in the welfare effects
section (V.C.2), although we are seeing
effects at current nitrogen deposition
rates, for the above reasons we believe
that it is not technically or practicably
feasible to identify a basis for
concluding that the existing NO2
increments are inadequate to provide
protection against the types of adverse
effects on ecosystems that may occur in
some areas notwithstanding compliance
with the NAAQS. In particular, it is not
possible to determine a different level of
increment protection that would define
a significance level for ecosystem effects
associated with emissions of NOX.
Currently available information does not
provide a nationally applicable,
quantitative basis for revising the levels
of the existing NO2 increments. The
EPA solicits comment on possible
approaches that should be considered,
including the concept of critical loads,
for further evaluating the existing NO2
increments. However, under today’s
action, we are not proposing any
changes to those increments.
(5) Qualitative consideration of
factors. Because we cannot use the
effects data to quantify an alternative
level of increase to the ‘‘safe harbor’’
that protects air quality values, health
and welfare, and parks while ensuring
economic growth consistent with the
preservation of clean air resources, we
must instead make a qualitative
judgment whether the existing
increments or some alternative meets
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the applicable factors. In this situation,
we believe that determining the
increment levels that satisfy the factors
applicable under section 166(c) is
ultimately a policy choice that the
Administrator must make, similar to the
policy choice the Administrator must
make in setting a primary NAAQS ‘‘with
an adequate margin of safety.’’ See Lead
Industries Ass’n v. EPA, 647 F.2d 1130,
1147 (DC Cir. 1980) (where information
is insufficient to permit fully informed
factual determinations, the
Administrator’s decisions rest largely on
policy judgments). Using a similar
approach is warranted because both
section 109 and section 166 place great
weight ‘‘in the Administrator’s
judgment’’ in making choices regarding
an adequate margin of safety or
protecting against any effects that may
still occur—both areas of inquiry
characterized by great uncertainty.
Thus, in the process for setting NAAQS,
the Administrator looks to factors such
as the uncertainty of the science, the
seriousness of the health effects, and the
magnitude of the environmental
problem (isolated or commonplace).
E.g., 62 FR 38652 (July 18, 1997) (PM2.5
NAAQS).
A pure environmental protection
analysis (protecting AQRVs, health and
welfare, and parks) might suggest that
we permit no or minimal increases in
some areas because there are some data
indicating that an effect may be
attributable to NOX emissions. However,
as explained earlier, we do not believe
that Congress intended for the PSD
program to eliminate all adverse effects.
Thus, rather than just seeking to
eliminate all effects, we must attempt to
identify a level of increase at which any
additional effects beyond existing (or
baseline) levels would be ‘‘significant’’
and protect against those potential
effects. Furthermore, we need to ensure
that our increments provide room for
economic growth. Congress intended for
EPA to weigh these considerations
carefully and establish regulations that
balance economic growth and
environmental protection.
In making this policy judgment, we
give particular weight to the policy
judgment that Congress made when it
set the statutory increments as a
percentage-of-the-NAAQS. In section
166 of the Act, Congress directed that
EPA study the establishment of PSD
regulations for other pollutants for
which Congress did not wish to set
standards at the time. Congress’ own
reluctance to set increments to prevent
significant deterioration of air quality
due to emissions of NOX, and the
provisions ensuring time for
Congressional review and action,
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suggest that Congress intended for EPA
to avoid speculative judgments about
the science where data is lacking.
Having conducted such a study and
finding difficulty establishing a direct
relationship between adverse effects and
particular levels of increase in
pollution, we believe it is appropriate to
consider the approach that Congress
used. Thus, in the absence of specific
data showing that a marginal increase of
a particular level below the ‘‘safe
harbor’’ would better protect health,
welfare, parks, and air quality values,
we give weight in our qualitative
analysis of the factors applicable under
section 166(c) to the method that
Congress used to establish the statutory
increments.
In making this qualitative judgment,
we also consider the overall regulatory
framework that we have established in
the PSD regulations for NOX. This
framework includes a case-by-case
analysis of each permit application to
identify additional impacts (e.g., soils
and vegetation), a special review by the
FLM of potential adverse effects on air
quality values in parks and special
areas, and a requirement that all new
and modified sources install BACT. In
addition, the area classification system
ensures that there will be economic
growth in particular areas that are
consistent with the values of each State
and individual communities within
States.
When coupled with the overall
framework of PSD regulations
applicable to NOX, we believe the ‘‘safe
harbor’’ approach for setting the
increment levels is sufficient to satisfy
the factors applicable under section
166(c). This approach ensures economic
growth and that each area receives a
basic level of protection consistent with
Congressional policy and an additional
case-by-case review of effects on air
quality values and parks and special
areas. Under this circumstance, we see
no basis to deviate from the approach
established by Congress for the statutory
increments. Thus, we propose to retain
the existing NO2 increments that were
established at the ‘‘safe harbor’’ level
using the percentage-of-NAAQS
approach. We request comment on this
proposal, the supporting analysis, and
reasoning described above.
b. Additional Increments
(1) Pollutant form for which
increments for NOX are set. Another
disputed issue in the EDF v. EPA case
was EPA’s action in 1988 to establish an
increment for only one form of NOX,
i.e., NO2. We promulgated increments
for NO2 in 1988 because NO2 was the
only form of NOX for which we had
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established a NAAQS at that time.
However, in EDF v. EPA, the court held
that section 166(c) of the Act
‘‘commands the Administrator to
inquire into a pollutant’s relation to the
goals and purposes of the statute, and
we find nothing in the language or
legislative history suggesting that this
duty could be satisfied simply by
referencing the ambient standards.’’ 898
F.2d at 190. Thus, in this rulemaking
action on remand, we must evaluate
whether, considering the factors
applicable under section 166(c), we
should promulgate additional
increments for other forms of NOX.
Under the ‘‘contingent safe harbor’’
approach discussed above, we begin our
analysis with ‘‘safe harbor’’ increments
that only address increases in ambient
NO2 concentrations. Since 1988, EPA
has not identified a basis to establish a
NAAQS for any form of NOX other than
NO2. Thus, it remains the case today
that the only NAAQS established for
NOX are the current NO2 NAAQS which
have not changed since 1971. We
believe that increments based on the
same pollutant for which we have a
NAAQS are the ‘‘safe harbor’’ for
purpose of this rulemaking. Establishing
increments for this form of NOX is ‘‘at
least as effective’’ as the statutory
increments in section 163 of the Act.
Congress established statutory
increments in section 163 for only those
forms of PM and sulfur oxides for which
we had promulgated a NAAQS.25 As
discussed above, the need for an
increment necessarily derives from the
establishment of a NAAQS, which is the
basic measure of air quality under the
CAA. Thus, an increment based on this
basic measure of air quality is ‘‘at least
as effective’’ as the statutory increments
in section 163 of the Act. The court in
EDF v. EPA rejected the argument that
increments based on the same form of
NOX as the NAAQS were not ‘‘as
effective as’’ the increments in section
163. 898 F.2d at 190.
We noted earlier in this preamble that
seven oxides of nitrogen are known to
occur in the atmosphere. (See footnote
9.) Among these, EPA recognizes the
significant role that nitrates play in
many of the indirect welfare effects of
NO2. Nitrate is a principal contributor to
the effects on ecosystems of both
nitrogen deposition (eutrophication and
acidic deposition) and visibility
impairment (regional haze). As such,
25 Since that time, we have refined the original
NAAQS for PM (then measured as TSP) to focus on
coarse (PM10) and fine (PM2.5) particulate matter.
We subsequently established increments for PM10
in accordance with section 166(f) of the Act. 58 FR
31622 (June 3, 1993). We are considering
establishing increments for PM2.5.
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nitrates conceivably could represent a
form of NOX which should be
considered for regulation under the PSD
increments. For several reasons,
however, EPA believes that it is not
necessary to adopt individual
increments for nitrate.
First, nitrate compounds found in the
atmosphere generally are formed from
the oxidation of NO and NO2 as they are
transported in the atmosphere.26 Thus,
the existing NO2 increments can
generally be viewed as a limiting factor
in the formation of nitrate
concentrations downwind. By limiting
the allowable increase in ambient
concentrations of NO2 in the immediate
area surrounding proposed new or
modified PSD source, some limit can
effectively be placed on downwind
NO3· formation as well.
Another consideration is that ambient
nitrate can often exist in the atmosphere
in particulate form, e.g., ammonium
nitrate or nitric acid vapor. Nitric acid
(a nitrate formed through the gas-phase
reaction of NO2 and OH), which plays
a key role in acid rain, in its gaseous
phase can also react with airborne
particle surfaces to form nitrate salts.
When ambient concentrations of
ammonia and nitric acid are sufficiently
high, ammonium nitrate can be formed.
Nitrate particulates contribute to
regional haze. The EPA believes that it
can more effectively regulate nitrates
particulate under the PM program. In
fact, the effects of nitrate particulate
were considered in setting the NAAQS
for PM2.5 and will be considered in the
development of the upcoming PSD
increments for PM2.5 as well.
Finally, EPA does not believe that
sufficient information is available to
adequately establish levels for nitrate
increments, even if it were to determine
that the establishment of increments for
nitrate are necessary to satisfy the
factors applicable under section 166(c).
We described the difficulties of
establishing alternative increment levels
using the available information in the
previous section.
In the absence of information showing
that increments based on the same
pollutant of the NAAQS fail to protect
air quality values, health and welfare,
and parks and special areas, from
emissions increases associated with new
and modified PSD sources, we propose
to retain the ‘‘safe harbor’’ increments
without adopting additional increments
for NOX. Under these circumstances, the
NAAQS provides a reasonable
benchmark for identifying the pollutant
26 Another source of nitrates, not associated with
emissions of NOX, is the nitrification of ammonium
by bacteria in stream beds.
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to be used in an increment. Section
160(1) of the Act is expressed by using
the NAAQS as a benchmark and also
uses standards that mirror the standards
applicable to the NAAQS-setting
process—‘‘protect public health and
welfare.’’ The court in EDF v. EPA
rejected use of the NAAQS as the ‘‘sole
basis’’ for deriving the increments for
NOX but did not preclude EPA from
adopting only increments based on the
same pollutant as the NAAQS when
EPA has determined that such
increments are sufficient to satisfy the
special values embodied in the factors
applicable under section 166(c) of the
Act. See 898 F.2d at 190.
Thus, we propose to retain the NO2
increments and do not propose to
establish additional increments for other
forms of NOX. We request comment on
this proposed action and our basis for it.
(2) Time periods for increments. In
accordance with the court’s opinion in
EDF v. EPA, we have also evaluated
whether we should promulgate
additional NO2 increments based on a
short-term averaging time. In the 1988
rule, EPA did not set short-term NO2
increments because a short-term
NAAQS for NO2 that would define
short-term air quality for NO2 did not
exist. However, the court directed us to
evaluate whether, considering the
factors applicable under section 166(c),
we should promulgate additional
increments for short-term averaging
times. 898 F.2d at 190.
Under the ‘‘contingent safe harbor’’
approach discussed above, we begin our
analysis with the ‘‘safe harbor’’
increments that are based on the same
annual averaging time used in the
NAAQS. Since 1988, EPA has not found
cause to promulgate a NAAQS for any
averaging time shorter than annual.
Thus, since this is the only averaging
time used in the current NAAQS, we
consider an increment that employs this
averaging time to be a ‘‘safe harbor’’ that
is ‘‘at least as effective’’ as the statutory
increments in section 163 of the Act.
The increments listed in section 163 of
the Act are based on the same averaging
times that were contained in the
NAAQS at the time Congress adopted
this provision. The NAAQS are the
basic measure of air quality under the
CAA. Therefore, an increment that uses
this standard as a benchmark is ‘‘at least
as effective’’ as the statutory increments
in section 163 of the Act. The court in
EDF v. EPA rejected the argument that
an increment based on the same
averaging time as the NAAQS was not
‘‘as effective as’’ the increments in
section 163. 898 F.2d at 190.
We have further analyzed whether a
short-term increment is necessary to
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8903
satisfy the factors applicable under
section 166(c) of the Act. Based on this
review, we believe that an annual
average increment for NO2 is sufficient
to protect air quality values, health and
welfare, and parks and special areas
from potential short-term effects. Thus,
we propose to retain the existing annual
NO2 increments and do not propose to
adopt additional increments for shorter
time periods.
The same reasons that supported our
decision not to set a short-term NAAQS
for NO2 weigh against setting a shortterm NO2 increment. We have not
identified health effects from short-term
exposure to NO2 that occur in areas in
attainment with the NAAQS. In
addition, we do not have sufficient
information to conclude that the welfare
effects within the scope of our review
are caused solely by short-term NOX
concentrations.
In our last review (1995–1996) of the
NO2 NAAQS, EPA reviewed the shortterm effects of NO2 on human health
and concluded that a short-term
standard was not justified. With regard
to public health, the Administrator
concluded that the annual standard of
0.053 ppm NO2 provides ‘‘substantial
protection’’ against the identified health
effects (mild changes in pulmonary
function or airway responsiveness in
sensitive individuals) associated with
short-term peaks occurring in the range
of 0.2 to 0.5 ppm—almost one order of
magnitude higher than the annual
standard. 60 FR 52875, 52879–80
(October 11, 1995). The adequacy of the
annual standard to protect against these
potential short-term effects was further
supported by the absence of
documented effects in some studies at
higher concentrations (3 ppm to 4 ppm).
The Administrator also took into
account that where the annual NO2
standard is attained—currently all areas
of the country—the occurrence of 1hour NO2 values greater than 0.15 ppm
would be unlikely. Id.
With respect to public welfare effects
from NO2, the Administrator also
concluded that the impact on terrestrial
vegetation from short-term exposures to
NO2 under existing ambient levels is
insignificant and did not warrant a
short-term standard (1995 Staff Paper, p.
91). The Administrator also considered
the welfare impacts from nitrates during
the last review of the NO2 NAAQS.
Although we believe we are not
required to consider these PM impacts
in selecting measures to prevent
significant deterioration of air quality
due to emissions of NOX under section
166(a), we find it noteworthy that none
of the welfare impacts from nitrates
were attributed to short-term exposure
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to nitrates and that significant
uncertainties in the data were
recognized. Even in those cases where
nitrogen deposition was shown to cause
episodic or ‘‘short-term’’ effects, the
problem was typically the result of a
long-term accumulation of nitrogen
compounds that were released suddenly
to the ecosystem (e.g., snowmelt runoff
to lakes and streams) rather than the
result of short-term concentrations of
nitrogen compounds in the air.
The conclusions from the last NAAQS
review regarding the lack of a
quantitative basis for establishing any
short-term NO2 standard were also
reported in an EPA document issued in
1997, entitled ‘‘Nitrogen Oxides:
Impacts on Public Health and the
Environment.’’ Id. at 33 (‘‘While shortterm effects from NO2 are documented
in the scientific literature, the available
information is insufficient to provide an
adequate scientific basis for establishing
any specific short-term standard.’’).
Additionally, independent of the
short-term exposure issue, as discussed
in another section of this preamble, EPA
has previously identified problems that
preclude the establishment of a national
standard to protect against
eutrophication and acid deposition.
These include: (a) The site-specific
nature of such impacts (e.g., existing
levels of nitrogen in the ecosystem and
sensitivity of vegetation to additional
inputs), which cannot be addressed by
a uniform national standard; and (b)
significant uncertainties over the level
of contribution of NOX sources to
nitrogen deposition, determining
whether an ecosystem was nitrogen
saturated, and a lack of data establishing
the quantitative levels of concern. 60 FR
52874, 52884 (October 11, 1995).
EPA has also recognized that NOX
results in the formation of ozone and
nitrate particulates under certain
conditions. Although ozone, PM10, and
PM2.5 have short-term NAAQS to protect
against public health effects associated
with short-term exposure to these
pollutants, EPA does not consider the
impacts from these criteria pollutants,
because it interprets section 166 to
require consideration of these criteria
pollutants separate and distinct from the
duty to consider NOX.
Thus, considering the factors
applicable under section 166(c), EPA’s
proposed option 1 is to retain the
annual average increments and not
establish any additional increments
based on a shorter averaging time. We
request comment on this option and our
basis for proposing it.
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B. Regional Cap and Trade Program
EPA’s second proposed option for
achieving the goals and objectives set
forth in the Act to prevent significant
deterioration of air quality due to
emissions of NOX is to create an
incentive for the States to implement a
market-based cap and trade program to
achieve the goals and purposes of PSD.
Under this approach, we would permit
States that adopt a cap and trade
program under specific CAA programs
being considered by EPA to implement
this cap and trade program in lieu of an
increment system for NOX. Thus, States
would not need to require sourcespecific compliance demonstrations for
the NO2 increments under their PSD
regulations. This cap and trade program
would have to be included in the EPAapproved SIP for each affected State and
would have to satisfy the requirements
of sections 166(c) and 166(d) of the Act.
Under this option, we propose a
finding that a cap and trade program
with specific elements and
characteristics would be sufficient to
fulfill the requirements of section 166,
and thus obviate the need for States to
implement the NO2 increments and
conduct case-by-case analyses of
whether a proposed new or modified
major source would cause or contribute
to an exceedance of an increment. We
propose to allow States to request
elimination of the NO2 increments from
their PSD programs following their
submission of a SIP revision that
contains a cap and trade program with
these specific elements.
EPA believes that the requirements of
section 166 to prevent significant
deterioration of air quality could be
satisfied if States were to adopt the
model EGU cap and trade program
proposed for States in the eastern U.S.
in the CAIR. Under the CAIR proposal,
specific States in the East and Midwest
would be required to submit SIPs that
contain controls sufficient to eliminate
specified amounts of NOX emissions in
order to reduce emissions contributing
to nonattainment of the PM2.5 and ozone
NAAQS in downwind States. The EPA
indicated in the CAIR proposal that
States subject to CAIR have the option
to achieve these reductions by
participating in a regional cap and trade
program for EGUs that would be
administered by EPA. Because the CAIR
cap and trade program would require all
of the sources participating in the
program to collectively meet a NOX cap,
and because this NOX cap is set at a
level that ensures significant NOX
reductions from the source categories
covered by the cap, we believe it would
be equivalent to or better than the
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existing NO2 increment approach which
allows increases in emissions. Thus,
EPA proposes that States participating
in this program could rely upon it as a
substitute for implementing the existing
increment system for NOX.
EPA does not propose to adopt or
require the States to implement such a
cap and trade program under legal
authority contained in the statutory
provisions for PSD. However, we
believe the air quality benefits that such
a program would provide could serve to
ensure that no significant air quality
deterioration will occur. Based on our
analysis supporting the CAIR proposal,
we believe we can show that the CAIR
model cap and trade program, when
implemented, will achieve reductions in
NOX emissions from EGUs that are
sufficient to compensate for projected
increases in NOX emissions from new or
modified major sources in other source
categories.
1. Description of Cap and Trade
Programs
A cap and trade program is a marketbased system that is designed to achieve
required emissions reductions as
needed to reach a particular emissions
goal or cap within a predetermined
geographical area. The basis for the
overall emissions cap is typically to
meet specific air quality objectives for
the area or an affected downwind area.
The emissions ‘‘cap’’ limits the total
mass emissions for the area of interest
by providing a limited number of
emission allowances—each allowance
authorizing the emission of a specific
amount (e.g., under title IV, one Acid
Rain Program allowance authorizes the
emission of one ton of SO2).27 Setting
the emissions cap properly is key to
achieving the desired environmental
outcome. The allowance trading market
provides a flexible mechanism for
sources to find the least-cost reductions
necessary to meet the cap.
For example, a source with a total of
400 allowances (400 tons of NOX
emissions) that is currently emitting 700
tpy of NOX could, factoring in economic
considerations, meet its requirement to
turn in allowances equal to its
emissions by (1) directly reducing
current emissions by 300 tons via the
installation of controls, fuel switching,
reducing utilization, etc., (2) purchasing
allowances from other capped sources
within the prescribed region that have
controlled their emissions beyond the
level needed to meet their requirement
to turn in allowances equal to their
27 Under CAIR, EPA has proposed that more than
one Acid Rain allowance would have to be turned
in for each ton of SO2 emissions.
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emissions, or (3) some combination of
these two approaches.
In the case of the NOX SIP Call, the
regionwide emissions cap was
apportioned to individual States,
thereby creating State-level ‘‘emission
budgets.’’ Typically, the emissions from
an entire sector are ‘‘capped’’ to ensure
that emissions are not simply shifted
from a capped unit to one that is not
subject to the cap.
Once an emissions goal or cap is
established for an area, the regulating
authority allocates emission allowances
to individual sources. In the case of the
Acid Rain Program and the NOX SIP
Call, EPA and individual States,
respectively, allocate the emission
allowances to the sources. Sources
comply with cap and trade programs by
holding enough allowances in their
account to cover their reported
emissions. This is independent of the
allocation process, as the allowance
trading market allows sources to reduce
their emissions or purchase additional
emission allowances.
A cap and trade program is generally
more cost-effective when more sources
are eligible to participate and
allowances can be traded without
restriction. For example, in a regionally
based cap and trade program, when
affected States allow the sources within
their jurisdiction to participate in the
opportunity for emissions trading
anywhere within the defined region,
this trading affords the flexibility
needed to enable sources to achieve
established emission goals at lowest
possible cost and encourage least-cost
compliance over the entire region.
EPA and States have had considerable
success achieving specific air quality
goals through the implementation of cap
and trade programs. Title IV of the 1990
Amendments established the Acid Rain
Program to address the deposition of
acidic particles and gases.28 The Acid
Rain Program utilizes a market-based
cap and trade approach to require power
plants to reduce SO2 emissions to 50
percent of the 1980 emission levels. At
full implementation after 2010,
emissions will be limited (i.e.,
‘‘capped’’) to 8.95 million tons in the
contiguous U.S. Individual existing
units are directly allocated their share of
the total emissions allowances, each
allowance being an authorization to
emit a ton of SO2.
The cap and trade program under the
Acid Rain Program has created financial
incentives for electricity generators to
28 The Acid rain Program requires a phased
reduction of emissions of SO2 (and, to a lesser
extent, NOX) from power generators that sell
electricity.
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look for new and low-cost ways to
reduce emissions, and to improve the
effectiveness of pollution control
equipment, at costs much lower than
predicted. The cap on emissions,
automatic penalties for noncompliance,
and stringent emissions monitoring and
reporting requirements ensure that
environmental goals are achieved and
sustained, while allowing for flexible
compliance strategies that take
advantage of trading and banking. The
level of compliance under the Acid Rain
Program continues to be quite high,
measuring over 99 percent.
In 1998, EPA promulgated a rule
determining that 22 States 29 and the
District of Columbia in the eastern half
of the country significantly contribute to
1-hour and 8-hour ozone nonattainment
problems in downwind States.30 This
rule, generally known as the NOX SIP
Call, required those affected
jurisdictions to revise their SIPs to
include NOX control measures to
mitigate the significant ozone transport.
The NOX SIP Call requires ozone season
NOX reductions which EPA determined
by projecting NOX emissions to 2007 for
all source categories, and then reducing
those emissions through controls that
EPA determined to be highly costeffective.31 The affected States were
required to submit SIPs providing the
resulting amounts of emissions
reductions.
Under the NOX SIP Call, States have
the flexibility to determine the mix of
controls to meet their emissions
reductions requirements. However, the
rule provides that if the SIP controls
EGUs, then the SIP must establish a
budget, or cap, for EGUs. The EPA
recommended that each State authorize
a trading program for NOX emissions
from EGUs. Consequently, each State
chose to adopt a cap and trade program
based on a model rule developed by
EPA. Some States essentially adopted
EPA’s full model rule ‘‘as is,’’ while
29 The original jurisdictions were: Alabama,
Connecticut, Delaware, District of Columbia,
Georgia, Illinois, Indiana, Kentucky, Maryland,
Massachusetts, Michigan, Missouri, New Jersey,
New York, North Carolina, Ohio, Pennsylvania,
Rhode Island, South Carolina, Tennessee, Virginia,
West Virginia, and Wisconsin. Subsequent court
and EPA actions have slightly reduced the affected
area.
30 See ‘‘Finding of Significant Contribution and
Rulemaking for Certain States in the Ozone
Transport Assessment Group Region for Purposes of
Reducing Regional Transport of Ozone; Final Rule,’’
63 FR 57356 (October 27, 1998). The EPA also
published two Technical Amendments revising the
NOX SIP Call emission reduction requirements (64
FR 26298, May 14, 1999; and 65 FR 11222, March
2, 2000).
31 Under the NO SIP Call, States are only
X
required to provide for the prescribed emissions
reductions during the summer ozone season, and
not year-round.
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other States adopted the model rule
with changes to the sections that EPA
specifically identified as areas in which
States may have some flexibility.
Following the NOX SIP Call, EPA
carried out a broader assessment to
determine the role of transported
emissions from upwind States in
contributing to unhealthy levels of fine
particles (PM2.5) and 8-hour ozone in
downwind States. As a result, on
January 30, 2004, at 69 FR 4566, EPA
proposed to find that 29 States and the
District of Columbia contribute
significantly to nonattainment of the
NAAQS for fine particles (PM2.5) and/or
8-hour ozone in downwind States
through transport of both NOX and SO2
emissions. In this proposal, originally
known as the IAQR, EPA expressed its
intent to assist States to attain the
NAAQS in a way that is timely,
practical, and cost effective, by
proposing emissions reduction
requirements for NOX and SO2, that
would apply to upwind States.
The proposed IAQR (now known as
the CAIR) requires certain States in the
eastern portion of the U.S. to submit SIP
measures to ensure that emissions
reductions are achieved as needed to
mitigate transport of PM2.5) and/or
ozone pollution and its main
precursors—SO2 and NOX—across State
boundaries.32
The proposed CAIR focuses on States
whose emissions are significantly
contributing to fine particle and ozone
pollution on other downwind States in
the eastern half of the U.S. The EPA
identified emissions control
requirements in the form of emissions
budgets for 29 States and the District of
Columbia on the basis of their
contribution to nonattainment problems
in the eastern half of the U.S. In
determining States’ emissions reduction
requirements, EPA considered both the
level and timing of the emissions
budgets for the electric power industry
at a regional level and State level. The
EPA calculated the amount of each
State’s NOX emissions reduction
requirement based on reductions that
were determined to be highly cost32 Clean Air Act section 110(a)(2)(D) requires SIPs
to contain adequate provisions prohibiting air
pollutant emissions from sources or activities in
those States that contribute significantly to
nonattainment in, or interfere with maintenance by,
any other State with respect to a NAAQS. EPA
proposed the IAQR requiring SIP revisions in 28
States and the District of Columbia to reduce SO2
and/or NOX emissions, which are important
precursors of PM2.5 (NOX and SO2) and ozone
(NOX).
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effective for large electric generating
units (EGUs).33
EPA’s proposal to use a cap based on
highly cost-effective reductions from the
electric power industry resulted in part
from the fact that we had relatively
complete information with respect to a
number of key factors for that industry,
that was not available for other sources.
In addition, the electric power industry
emits relatively large amounts of the
relevant emissions. This factor was
considered particularly important in a
case where the Federal government was
proposing a multi-State regional
approach to reducing transported
pollution.
As proposed, each affected State may
independently determine which
emissions sources to subject to controls,
and which control measures to adopt to
satisfy its reduction requirements.
Alternatively, States were given the
opportunity to participate in a regional
cap and trade program to cap emissions
from EGUs. The EPA indicated that it
would administer the cap and trade
program in a manner similar to the NOX
SIP Call program.
If the State chooses to control EGUs,
then it must establish a budget—that is,
an emissions cap—for those sources.
The State may allow them to participate
in the interstate cap and trade program,
and, if so, the State must follow EPA’s
model rule, which contains required
provisions including monitoring and
reporting, applicability, and penalties. If
a State wants to control EGUs but does
not want to allow EGUs to participate in
the interstate cap and trade program, the
State has flexibility to do so, but the
State EGU rule must contain certain
minimum requirements such as capping
emissions from EGUs and requiring part
75 monitoring.
A supplemental notice, issued on
June 10, 2004 (69 FR 32684), provided
additional detail on establishing State
emissions budgets (i.e., emissions
reductions requirements) and significant
additional information concerning
EPA’s model cap and trade program for
EGUs, including, among other things,
requirements for adopting the model
cap and trade rules, flexibility afforded
to States in adopting certain program
features, and proposed regulatory
language covering monitoring,
recordkeeping, and reporting
requirements.
33 EPA based its emissions reduction
requirements on reductions from large EGUs, i.e.,
boilers and turbines serving an electric generator
with a nameplate capacity exceeding 25 MW and
producing power for sale. EPA further proposed
that its model regional cap and trade program
would apply to these units.
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The emission reductions for NOX
expected under the CAIR are significant.
Under the CAIR, EPA proposes to
implement highly cost-effective
reductions in two phases, with a Phase
I compliance date of January 1, 2010,
and a Phase II compliance date of
January 1, 2015. When fully
implemented, NOX emission reductions
would be substantial, measuring about
1.5 million tons in 2010 and 1.8 million
tons in 2015. This represents a
reduction approximately 65 percent
below current NOX levels.
2. Using a Cap and Trade Program in
Lieu of an Increment System for NOX
a. Cap and Trade Program Would Meet
Requirements of Section 166
We believe that EPA’s obligations to
promulgate pollutant-specific PSD
regulations for NOX under section 166
of the CAA could be satisfied by giving
States the option to implement a cap
and trade regulatory framework for
sources of NOX that achieves the
objectives of the PSD program. More
specifically, we believe that a State cap
on EGU NOX emissions at the level
described in the CAIR proposal for that
State would achieve emissions
reductions that would prevent
significant deterioration of air quality
from emissions of NOX. By participating
in this program and establishing a cap
on NOX emissions from EGUs at such a
level, we believe States could achieve
emissions reductions that produce
ambient air quality levels equivalent to
or better than the air quality allowed by
the existing NO2 increments and
associated regulations. Moreover, a
market-based cap and trade system
would provide greater certainty that a
specific level of emissions and air
quality will be attained and maintained.
Thus, we believe this may be an
effective alternative to an increment
system for NOX.
(1) Cap and trade framework fulfills
obligations under section 166. A cap
and trade framework has many elements
that satisfy the requirements of section
166(c), and such an approach would
qualify as an ‘‘other measure’’ that is
permissible under section 166(d). Thus,
we propose to allow States, in lieu of an
increment approach, to implement a cap
and trade framework that, in
combination with specific program
elements, would meet the requirements
of sections 166(c) and 166(d).
A cap on emissions that is allocated
to States through budgets and to
individual sources in the form of
tradeable allowances provides a
numerical measure against which
permit applications can be evaluated.
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Under a cap and trade approach, States
could prohibit the issuance of a PSD
permit to a new or modified source that
is subject to the cap unless the source
can ensure that it will have a sufficient
number of allowances to cover its
proposed emissions increase. In
evaluating a permit application for such
a source, a permit writer would only
need to verify that the permit requires
the source to turn in allowances equal
to its emissions each year.
Implementation of the cap in this
manner would not only satisfy the
‘‘numerical measure’’ requirement but,
for those sources subject to the cap,
would also be much more efficient and
less time-consuming than the current
process of conducting a source impact
analysis to make sure the proposed
emissions increase will not cause or
contribute to an increment violation.
Where a cap is used to achieve
emissions reductions necessary to offset
future growth by sources not subject to
the cap, the permit writer would need
to verify that emissions from the sources
subject to the cap remain below
required levels in order to issue a permit
to a source not covered by the cap.
For PSD purposes, the market-based
economic incentive inherent in a cap
and trade framework could also provide
a powerful stimulus for improved
control technology at those sources
subject to the cap. Even if new major
sources and major modifications subject
to the cap still have to meet
requirements for BACT, the market for
allowances could cause the facilities to
select a more stringent BACT than
would normally be selected. This, in
turn, could also have a carry-over effect
for subsequent BACT determinations
involving other new sources that are not
under the cap and trade program.
By allowing States to implement a
regional cap and trade system, we could
address the goal in section 160(4) of the
Act to assure that emissions in one State
do not interfere with the PSD program
in another State. By first developing a
stringent overall cap requiring
substantial reductions in NOX emissions
(e.g., 70 percent) for an entire region, the
cap and trade program provides
assurance to downwind States that
emissions from upwind States will be
effectively managed over time.
A cap and trade approach that
operates in concert with the PSD
preconstruction permit program would
continue to fulfill the PSD goal in
section 160(5) that any decision to
permit increased air pollution not be
made without careful evaluation and
public participation. For reasons
discussed below, major new sources and
major modifications will still require
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preconstruction permits and will have
to comply with existing requirements
for BACT. Thus, the public will have an
opportunity to comment on each permit.
However, the total allowable emissions
from sources subject to the cap would
be determined by regulatory authorities
at the time that the cap is first
developed. This process would still
involve the evaluation required under
section 160(5), but it would be
conducted in up-front modeling to
demonstrate the effectiveness of the cap,
well in advance of any case-by-case
permit review for sources subject to the
cap that must obtain allowances and
other sources outside the cap and trade
system that could not be permitted
without verification that emissions from
affected sources do not exceed the cap.
The public would have the opportunity
to comment on the cap and thus could
participate in any decision to establish
a cap that allows increased air
pollution. In the case of the NOX cap set
forth in the CAIR proposal, we
recognize that this comment
opportunity has passed. However, under
this option we are not proposing to
authorize States to adopt a program that
would allow an increase in air
pollution. We are proposing to allow
States to implement, in lieu of an NO2
increment, a cap and trade program that
would achieve overall reductions in
NOX emissions by reducing emissions
from certain sources to offset expected
increases from other sources.
In order to fulfill the minimum
requirements of section 166(d) under
the ‘‘contingent safe harbor’’ approach,
the cap selected for the cap and trade
program would have to be at least as
effective as the increments established
by statute for PM and SO2 in each
affected State. As discussed above, these
statutory increments were established as
a percentage of the NAAQS, which are
expressed as an ambient concentration
of air pollution. As a result, the PM and
SO2 increments are also expressed in
ambient concentration form and reflect
the maximum marginal increase in air
pollution concentration allowed in an
attainment area. Under the cap and
trade approach, we would allow States
to establish a cap on total NOX
emissions from specific sources,
expressed in terms of mass (tons) rather
than an ambient concentration (e.g.,
micrograms per cubic meter). To show
that a particular emissions cap on
specific sources is as effective as the
concentration-based increments for PM
and SO2, we could rely on ambient air
quality modeling that projects the
concentration in each part of a State that
would result from achieving a particular
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cap. A cap that maintains ambient
concentrations of NO2 within a certain
percentage of the pre-cap NO2 levels in
most areas (assuming no increment
violations currently exist) could then be
demonstrated to be at least as effective
as the statutory increments. However, to
the extent that modeling is not available
or is insufficient to make such a
showing, we request comment on how
we might use qualitative measures to
identify whether a particular cap is at
least as effective as the increments for
PM and SO2. We also request comment
on whether, in all cases or some cases,
this showing would be made inherently
because an emissions cap less than or
equal to the current level (or baseline
level) is prima facie evidence that
significant deterioration is being
prevented.
A cap at a level that is as effective as
the increments for PM and SO2 would
represent the ‘‘safe harbor’’ cap under
the ‘‘contingent safe harbor’’
interpretation we are proposing today
for section 166 of the Act. Under the cap
and trade option, once the safe harbor
is identified in this manner, we would
then analyze whether it satisfies the
requirements of section 166(c) by using
the same balancing test discussed above.
We would use this balancing test to
determine whether a cap other than the
‘‘safe harbor’’ cap is needed to protect
public health and welfare, as well as air
quality values, while also allowing for
economic growth consistent with the
preservation of existing clear air
resources.
We believe a cap and trade framework
is particularly well-suited for striking
the required balance between effective
environmental protection at a cost that
is not detrimental to economic growth.
The capping of total emissions of
pollutants throughout a geographic
region, and over a period of time,
ensures achievement of the
environmental goal while allowing
economic growth (new sources or
increased use of existing sources).
Within the constraints of the NAAQS
and the available increment, the
addition of new sources to the regulated
sector or an increase in activity at
existing sources can increase total
emissions even though the desired
emission rate control is in effect.
(2) Cap on NOX emissions proposed in
the CAIR would satisfy PSD
requirements. Using this analytical
approach, we propose to find that a cap
and trade program that caps NOX
emissions at the levels proposed in the
CAIR would fulfill the requirements of
section 166 of the Act. We believe a cap
on NOX of this magnitude would strike
the required balance between the
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environmental protection and the
economic growth goals of the PSD
program.
The proposed cap on NOX emissions
contained in the CAIR would be
established, under the authority of
section 110(a)(2)(D) of the Act, on the
basis of emissions reductions that can
be achieved by installing highly costeffective controls on EGUs. We believe
a cap on NOX emissions at this ‘‘highly
cost-effective’’ level would meet the
objectives of PSD by providing the most
protection for AQRVs, health and
welfare, and parks and other special
areas, while also ensuring economic
growth.
Our analysis in the CAIR proposal
showed that a cap on NOX emissions of
this magnitude in the relevant region
would produce improvements in
visibility and reduce acid deposition
and eutrophication of water bodies in
the eastern U.S. See 69 FR 4566, 4642
(Jan. 30, 2004) (Section X: Benefits of
Emissions Reductions in Addition to the
PM and Ozone NAAQS). A more
detailed discussion of these beneficial
effects is provided in a document
prepared for the CAIR and is entitled
‘‘Benefits of the Proposed Interstate Air
Quality Rule (January 2004).’’ This
document is available in the Air Docket
for this rulemaking and also at https://
www.epa.gov/air/interstateairquality/
tsd0175.pdf.
Allowing States to improve ecosystem
health in this manner, through a cap
and trade approach, would satisfy our
obligation to develop regulations under
section 166 of the Act that provide
protection for AQRVs, health and
welfare, and parks. Our analysis to date
indicates that a cap on NOX emissions
equivalent to the reductions proposed in
the CAIR for the eastern U.S. would
reduce adverse effects on AQRVs, health
and welfare, and parks in this region. 69
FR 32684, 32706 (June 10, 2004).
As noted above, visibility is an
important AQRV that is affected by
emissions of NOX. Reductions in
emissions of NOX at the level required
in the CAIR proposal are expected to
contribute to substantial visibility
improvements in many parts of the
eastern U.S., including Class I areas
such as the Great Smoky Mountains.
NOX emissions may also contribute to
effects on AQRVs, welfare, and parks
resulting from the deposition of nitrogen
onto land and water. The reductions in
NOX emissions required in the CAIR
proposal are anticipated to reduce
nitrogen deposition. Reductions in
nitrogen deposition will, in turn, reduce
acidification and eutrophication of
water bodies and have a positive impact
upon current eutrophic conditions in
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estuaries and coastal areas in the eastern
region of the country. Reductions in
nitrogen deposition are likely to have
positive effects on the health and
productivity of some forest systems.
Furthermore, reductions of this
magnitude would reduce deposition
that damages cultural monuments and
other materials.
In the CAIR proposal, we assessed the
quantitative impacts of the proposed
levels of NOX and SO2 reductions on the
acidification of water bodies. Areas
especially sensitive to acidification
include portions of the Northeast
(particularly the Adirondack and
Catskill Mountains, portions of New
England, and streams in the midAppalachian highlands) and
Southeastern streams. Modeling for the
CAIR indicated that as a result of the
proposed reductions in SO2 and NOX,
lakes in the Northeast and Adirondack
Mountains would improve in acid
buffering capacity. Specifically, we
found that no lakes in the Adirondack
Mountains were projected to be
categorized as chronically acidic in
2030 as a result of the reductions
proposed for the CAIR. In contrast, 12
percent of these lakes were projected to
be chronically acidic without the
emissions reductions envisioned in the
CAIR proposal. For Northeast lakes in
general, 6 percent of the lakes were
anticipated to be chronically acidic
before implementation of the proposal.
The NOX and SO2 reductions called for
in the CAIR proposal are expected to
decrease the percentage of chronically
acidic lakes in the Northeast to 1
percent.
We believe State implementation of
caps on NOX emissions at the levels set
forth in the CAIR proposal would
provide sufficient protection for AQRVs
in all the Class I areas in the eastern half
of the U.S. However, we request
comment on whether, even with caps of
this magnitude, States would need to
implement additional measures under
the model cap and trade program to
guard against localized adverse impacts,
particularly in Class I areas.
(3) Cap and trade approach would
provide ambient air quality analysis for
all sources. Under this cap and trade
program for EGUs, we do not believe it
will be necessary for any sources to
conduct a site-specific ambient air
quality analysis for NOX in order to
satisfy the requirements of section
165(a)(3) of the Act by showing that the
source will not cause or contribute to air
pollution in excess of the NAAQS or an
increment. In order to permit States to
adopt the CAIR model cap and trade
program in lieu of NO2 increments, EPA
or the States would have to perform an
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ambient air quality analysis to show that
the NOX caps applicable to each State
achieve enough reductions to ensure
that increases in NOX emissions from all
new or modified sources will not result
in an exceedance of the NO2 NAAQS or
cause significant deterioration of air
quality.
If States adopt a cap and trade system
and are not required to enforce the
increment, sources would not be
required under section 165(a)(3) to show
that they would not cause or contribute
to a violation of the NO2 increment.
Instead, the cap and trade program
would fulfill the function of the NO2
increments to prevent significant
deterioration of air quality. However,
the requirements of section 165(a)(3)
would still be satisfied because EPA,
rather than each individual source,
would demonstrate that the proposed
cap is sufficient to either prevent
significant deterioration of air quality
due to emissions of NOX or prevent a
violation of the NAAQS. Thus, it would
be redundant and unnecessarily costly
to require an individual source to
conduct a site-specific air quality
analysis under a cap and trade
approach. A source subject to the cap
would only need to show that it has
enough allowances to cover its
emissions. The total amount and
distribution of allowances would
already reflect the results of an air
quality analysis conducted by the
regulatory authority.
b. Using a Cap and Trade Program To
Streamline the PSD Permitting Process
The discussion above illustrates some
ways in which a cap and trade program
can enable substantial streamlining of
the PSD permit process. Such
streamlining, allowing applicants to
avoid various preconstruction review
requirements, could significantly reduce
both the resources needed to acquire the
necessary construction permit and the
time required to complete the
permitting process. Both are important
ways in which the PSD permit program
can be improved so long as adverse
impacts on the environment are not
allowed to occur as a result.
Even though the model cap and trade
program, as presently conceived, would
apply only to certain electric power
plants, the benefits of the streamlined
PSD permitting process would be shared
with all PSD applicants because of the
inherent ability of the cap and trade
program to enable a reduction in total
statewide NOX emissions from EGUs
sufficient to compensate for increases in
NOX emissions in the State from other
source categories of NOX emissions.
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Under the approach being proposed
today, States would have the option to
revise their implementation plans to
include the necessary regulations to
enable participation in and
implementation of the EPAadministered cap and trade program for
NOX under CAIR. Once the necessary
revisions are in place and in effect
under the applicable SIPs, EPA would
respond affirmatively to State requests
to use the cap and trade program in lieu
of source-specific compliance
demonstration for the NO2 increments.
The State would not be required to
conduct source-specific increment
analyses so long as the State continues
to implement the cap and trade
program.
The cap and trade program would not
provide a full exemption from the PSD
permitting process. All new major
stationary sources and major
modifications, including both EGUs
directly affected by the cap and trade
program and non-EGU major sources,
would still have to undergo some
preconstruction review for a PSD permit
prior to commencing construction on
new projects that result in a significant
net emissions increase for NOX. Such
permits would still need to include
emissions limitations based on BACT.
The primary benefit comes from the fact
that source-specific analyses for the NO2
increments and NO2 NAAQS would not
be required, as described in the above
subsection.34
We believe BACT must continue to
apply because this PSD requirement is
based on section 165(a)(4) of the Act,
not section 166, and cannot be fulfilled
by using a cap and trade approach. In
contrast, the ambient air quality analysis
that is based on section 165(a)(3) could
be conducted for all sources at the time
a cap is established and thus need not
be conducted again for each individual
permit.
The EPA believes other requirements
pertaining to air quality analyses might
also become unnecessary under a cap
and trade approach. For example,
statewide air quality improvements
shown to result from a cap and trade
program, as described elsewhere in this
34 State participation in a cap and trade
mechanism would not replace the statutory
requirement to meet the NAAQS for NO2 at the
local level, but rather helps achieve this
requirement through significant reductions in
background concentrations. While States will
continue to have the obligation and the authority
under the Act to assure that the NAAQS for NO2
is being met, we do not believe this needs to be
done on a source-specific basis under the PSD
permitting program, but rather through the ongoing
monitoring of ambient air quality using EPArecognized monitoring sites (showing current
attainment status) and possibly periodic modeling
assessments.
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preamble, may eliminate the need for
source-specific FLM review in Class I
areas. In its 1988 PSD regulations for
NOX, EPA applied this process to NOX
on the basis of section 166. We also
propose to retain this requirement under
the increment option discussed above.
However, we do not interpret section
165(d)(2)(C) to require this process for
NOX regulations established under
section 166. Section 165(d)(2)(C)
appears to be limited by its terms to
only PM and SO2. Nevertheless, we
believe we have the authority to apply
this FLM review process to NOX on the
basis of section 166. However, if the
requirements of section 166 are
otherwise fulfilled by a cap and trade
approach, we believe section 166 would
give us the discretion not to employ the
FLM review process described in
section 165(d)(2)(C).
We are also evaluating, and request
comment on, whether certain sourcespecific preconstruction requirements
could be satisfied by a cap and trade
approach. These include (1) the air
quality impact analysis required under
section 165(a)(6) that is codified in
regulations as the additional impacts
analysis (see, e.g., 40 CFR 52.21(o)); (2)
the analysis of air quality, climate and
meteorology, terrain, soils and
vegetation, and visibility required under
section 165(e)(3)(B); and (3) the air
quality monitoring requirement in
section 165(a)(7). In the latter case, PSD
applicants, where applicable, must set
up air quality monitoring stations and
begin collecting relevant air quality data
up to 12 months in advance of their
submittal of a complete PSD
application.
c. What Are Some Issues That Still Need
To Be Resolved?
EPA recognizes certain significant
issues that still need to be resolved
before a comprehensive proposal can be
set forth for public review and
comment. These issues are presented
here for public consideration.
(1) Failure to show ongoing statewide
downward trend in NOX emissions. The
EPA recognizes that it may not be
possible to show that NOX emissions
decreases in every State from CAIR at
least offset the expected contribution of
NOX emissions that non-EGU sources
make in the State. Consequently, in
States where the amount of NOX
reductions achieved through regulating
EGUs under the proposed cap and trade
program does not more than compensate
for increases at other sources of NOX, it
may be difficult to justify the use of the
proposed cap and trade program in lieu
of the existing increment system for
NOX.
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Preliminary air quality modeling by
EPA indicates that total NOX emissions
will generally decline on a statewide
basis across the nation. ‘‘Total NOX
emissions’’ includes contributions from
electric utilities, non-utilities, area
sources, and mobile sources (onroad,
nonroad). As proposed, the statewide
emissions budgets for NOX apply only
to affected EGUS. Sources not covered
under the regional cap and trade
program may face emissions limitations
stemming from other Federal or State
programs (e.g., Federal Motor Vehicle
Emissions Reduction Program) but
would not typically be restricted from
potential increases under any kind of
cap for the source category in general.
Thus, in cases where EPA’s modeling
cannot initially show a downward trend
in statewide NOX emissions for a
particular State because increases from
another source sector are exceeding the
reductions being generated by EGUS
under the cap and trade program, EPA
tentatively intends to announce the
continued applicability of that State’s
increment system for NOX as part of the
final rulemaking for today’s proposed
action.
As part of the comprehensive
modeling demonstration that EPA
intends to carry out to support this cap
and trade option, we will assess the
likelihood that total statewide NOX
emissions will continue to exhibit a
downward trend for future years. The
EPA believes that it will be necessary to
conduct periodic assessments (e.g., 10year intervals) of air quality trends for
NOX in order to continue justifying the
cap and trade program as a substitute for
the increment system for NOX. The EPA
seeks comments on the frequency of any
necessary periodic assessment, as well
as other possible mechanisms for
determining when adjustments may
need to be made to the cap and trade
program to retain its viability as a
replacement for the increment system or
other means of preventing significant air
quality deterioration for NOX.
(2) States in which baseline date has
not been set. While we believe, in
general, that the cap and trade program
would fulfill the function of the
increment to prevent significant
deterioration due to emissions of NOX,
we realize there are certain cases where
making this showing is more
complicated. The baseline against
which an increment is assessed is set at
the point of the first permit application
submittal by a new or modified source
located in the area. For areas that have
not yet had the first permit application
submitted, no baseline has been
triggered. For such areas, it is not
immediately clear that a cap and trade
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program is at least as effective as the
existing increment program. In the case
that such an area had its first permit
application submitted subsequent to the
realization of the emission reductions
anticipated from cap and trade in that
State, then an equivalency
demonstration between cap and trade
and the increment program becomes
more complicated.
One approach for addressing this
situation would be to maintain the
increment program as it currently exists
for States in which few or no baseline
dates have been set. We request
comment on this approach and any
other alternatives that address this
situation.
(3) Potential for localized adverse
impacts resulting from emissions
increases from new and modified
sources. The EPA is mindful of the
potential for localized impacts of
proposed sources and modifications
even where statewide emissions are
shown to be declining. In response to
this concern, we note that the January
30, 2004, CAIR notice of proposed
rulemaking addressed the issue of
localized adverse impacts. In that
notice, EPA indicated that experience
under the title IV Acid Rain Program
shows that ‘‘the combination of trading
with a stringent emissions cap results in
substantial reductions throughout the
region, with the greatest reductions
achieved in the areas where pollution
was originally the highest.’’ (69 FR
4629–30) The notice further stated that
other independent analyses have
supported the finding that emissions
trading under this type of program has
not resulted in the creation of localized
air quality problems.
We believe that this trend will
continue to occur as a result of the
extended use of a cap and trade
program, so that localized air quality
problems generally will not occur.
Nevertheless, there may be the potential
for localized adverse impacts, especially
around Class I areas, particularly when
a source of NOX locating near a Class I
area is not subject to a cap. While we
believe this situation is unlikely to
occur and are proposing to allow States
that participate in the cap and trade
programs under consideration to avoid
some case-by-case source impact
analyses under the preconstruction
review for PSD. Below, we solicit
comments on whether there is any need
for a limited source-specific analysis
under certain circumstances.
(4) Role of the Federal Land Manager
in the PSD permit process. The Act
provides that the FLMs have an
affirmative responsibility to protect any
AQRVs that have been identified for the
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Class I areas under their control. Section
165(d)(2)(B). Section 52.21(p) of the PSD
regulations requires notification of the
applicable FLM when there is a
potential for adverse Class I area
impacts, and it authorizes direct
involvement by the FLM in cooperation
with the applicable permitting authority
to identify any adverse effects on any
known AQRVs.
Although the cap and trade program
would significantly diminish the
possibility that PSD sources would
adversely impact a Class I area, in light
of the overall NOX reductions that
would occur, the potential for some
adverse impacts could still exist. In the
absence of individual source-specific air
quality analyses, which include data
that may be reviewed by the FLM early
in the permitting process to determine
the potential for adverse impacts, FLMs
would have to rely upon other means of
detecting such adverse impacts at a
point in the permitting process when
remedial action could be sought.
One possible remedy to this potential
problem is for EPA to include specific
criteria that, if not satisfied by a
particular PSD applicant, could enable
the FLM, in cooperation with the
permitting authority, to call for an
analysis of source impacts on the Class
I area. For example, regulatory
procedures could be established which
authorize an FLM to call for a source
impact analysis when a proposed new
or modified source locates within a
specified distance (e.g., 150 kilometers)
of a particular Class I area and air
quality in the area has shown little or no
improvement since the cap and trade
program took effect, as determined by
ambient monitoring data. The EPA seeks
public input on the above example, and
other possible parameters, that could
offer an effective way to ensure
continued protection against localized
adverse impacts from source growth
occurring under a cap and trade
program.
(5) States that are not affected by the
proposed CAIR. Many States are not
subject to the proposed CAIR, because
we believe they do not significantly
contribute to nonattainment or interfere
with maintenance of NAAQS in another
State. The EPA solicits comments on the
best way to address States that are not
subject to CAIR but that wish to
participate in an EPA-administered cap
and trade program, or that wish to
develop a State cap and trade program
to replace the increment system for NOX
currently in their State PSD program.
We believe that a nationwide EPAadministered cap and trade program
such as the Clear Skies Initiative could
replace the increment system for NOX.
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If that legislation is not enacted, States
that are not part of a regionally based
cap and trade program could develop a
State cap and trade program that could
be considered to meet the goals and
purposes of the Act for preventing
significant deterioration of air quality
due to emissions of NOX.
C. State Planning Approach
As a third option, we propose to allow
a State to submit a demonstration that
its SIP contains measures, in
conjunction with Federal requirements,
that would prevent significant
deterioration of air quality due to
emissions of NOX. Under this option,
we would establish a procedure for a
State to submit a SIP demonstration to
EPA to fulfill the requirements of
sections 166(c) and 166(d) of the Act. If
EPA determines that the SIP
demonstration meets the requirements
of section 166, then we would approve
the demonstration and allow the State to
implement the SIP in lieu of an
increment system for NOX. Thus, the
State planning approach, like the cap
and trade approach, would provide
States with an incentive to implement a
program to prevent significant
deterioration of air quality due to
emissions of NOX that may be more
effective than an increment system.
The State planning approach will be
implemented through States’ SIPs. Any
State choosing this option could submit
a demonstration that its SIP establishes
a clear planning goal, of the State’s own
design, to satisfy the section 166 PSD
requirements for NOX. To achieve the
goal of its SIP, a State could impose
NOX emission limitations on any
emissions sources it chooses, whether
new or existing, or demonstrate that
existing Federal and SIP limitations
have the appropriate effect.
While this approach gives States more
flexibility to design a program to
prevent significant deterioration of air
quality due to NOX emissions using a
system other than increments, the EPA
review and approval process would be
more time- and data-intensive. Under
this approach, the State would need to
provide a rigorous demonstration that
its planning goal and measures (in
conjunction with Federal requirements)
for meeting that goal are at least as
effective in preventing significant air
quality deterioration for NOX as the
increments for PM and SO2 (fulfilling
the safe harbor requirement of section
166(d)) and are consistent with the
criteria in section 166(c) and the goals
and purpose of PSD in section 160 of
the Act.
In contrast to the cap and trade option
described above, under this State
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planning option, we are not proposing
that the State must demonstrate that the
SIP includes a specific type of program
that we have already found to be
sufficient to satisfy the requirements of
section 166. However, under this State
planning option, we could establish a
specific planning goal that we find to be
sufficient to satisfy the requirements of
section 166. Thus, if the State
demonstrates that its SIP achieves our
recommended planning goal, this could
streamline EPA action on the plan.
However, if we do not establish such a
goal, a State would have to define this
on its own and demonstrate to EPA how
a program that achieves that goal would
satisfy the requirements of section 166
of the Act.
An example of a State planning goal
that we believe could meet the
requirements of section 166 would be a
goal that statewide NOX emissions from
all sources would remain at or below
the level observed in a specific baseline
year that, in turn, is identified to be
equivalent to the level of emissions that
results in significant deterioration. A
State could propose to achieve such a
goal by tracking and managing the
inventory of emissions from all sources
in the State to ensure that statewide
emissions of NOX do not increase above
this level. This approach would in effect
authorize a State to replace the NOX
increment requirement by
demonstrating that its SIP measures, in
conjunction with Federal measures,
achieve reductions in NOX emissions
from all sources that are sufficient to
offset projected increases from all types
of new and modified sources. We
believe this approach could be an
effective alternative to an increment
system. This kind of a State planning
approach would prevent significant
deterioration of air quality due to
emissions of NOX with a goal that
effectively permits no NOX emissions
increases from a specific baseline date.
The State would have to track its
inventory of emissions and establish
control measures on all types of sources
(new and existing) as appropriate to
meet the goal.
1. Description of State Planning
Approach
This State planning option allows
States to prevent significant
deterioration of air quality due to NOX
emissions through specific statewide
control strategies. In developing its
approach, the State may consider broad
scientific research and assessment of
various means of meeting air quality
management goals (visibility progress,
emission density requirements, or other
markers).
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The State planning approach may be
workable for source categories such as
mobile and area sources, for which a
budget approach is unproven and for
which the available emissions
quantification techniques are too
imprecise to support the budget
approach. As stated before, a State may
achieve its SIP goal by controlling NOX
emissions from any emissions sources it
chooses. The State’s control
requirements, when implemented, must
prevent significant deterioration of air
quality due to NOX emissions.
Under this option, a State may choose
to develop its own NOX emissions cap,
with approval based on the cap’s
meeting the requirements of sections
166(c) and 166(d). That is, for purposes
of this proposed rule, the State would
not be subject to an EPA-determined
NOX budget. The State would be
responsible for tracking its NOX
emissions and for identifying and
reacting to needed corrections in its
allowable NOX emissions.
Under the State planning option, SIPs
could include emission targets that
provide for growth from new and
modified sources. SIPs should be
required to track actual emissions
increases from new and modified
sources and provide mechanisms for
addressing areas that exceed these
projected increases. The State is
manager of the air quality resource and
decides how much growth it will allow
consistent with the requirement to
prevent significant deterioration of air
quality.
a. SIP Requirements
Under the State planning option, a
State may impose NOX emissions
control requirements in the form of a
NOX emission rate limit, a specified
type of technology, or even a cap on
NOX emissions. However, to
demonstrate that its plan is at least as
effective as the increments for PM and
SO2, the State must demonstrate
through its emissions inventory that its
control requirements are adequate from
an air quality standpoint.
Critical to SIP planning are the
elements of accountability and
emissions tracking. To ensure that the
SIP goal is achieved, the State planning
approach requires an accurate baseline
emissions estimate. Then, to
demonstrate the amount of emissions
control from the controlled sources, the
State must take into account the amount
of emissions attributable to the sources
or source category both in the base case
year and in the control case. The SIP
must include monitoring,
recordkeeping, and reporting
requirements. Unlike under the cap and
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trade option (option 2), under the State
planning option (option 3), the State
must bear the responsibility for
monitoring progress and tracking
emissions.
The EPA is soliciting comment on
what requirements are needed to ensure
that the SIP goal is met. Overarching
considerations include whether the
requirements: (1) Provide certainty that
all emissions that are controlled
pursuant to this option are adequately
controlled; (2) ensure that controls will
continue to be adequate in future years;
and (3) ensure that the control
requirements can be feasibly
implemented.
Pursuant to section 166(c), the State
goal must provide specific numerical
measures against which permit
applications may be evaluated. Under
option 3, we propose that each SIP
demonstration must include a NOX
emissions inventory for its baseline year
(1990 or other). The State will have to
weigh its projected reductions against
its projected increases (so as to allow for
growth) over the next 10 years. Each
State will need to demonstrate that the
objectives of the statutory PSD program
for NOX are being met, for example, by
demonstrating that NOX increases are
less than or equal to NOX reductions at
the end of a 10-year period, or by some
other scheme that can accommodate
significant growth of emissions, which
is particularly anticipated in the
western U.S. Based on the State’s
demonstration through statewide
modeling and analysis that it will meet
the SIP goal, the State would be
permitted to waive some of the case-bycase analysis for new and modified
major sources subject to PSD
preconstruction permitting.
b. Benefits of State Planning Approach
The State planning approach could
effectively serve in the same way that an
increment system does to prevent
significant air quality deterioration,
with the added benefit of eliminating
the need for certain case-by-case source
analyses as currently required for
sources applying for preconstruction
permits under State PSD programs.
Depending on how a program is
designed by the State, a State planning
approach could not only prevent
significant air quality deterioration but,
while not required to do so, also provide
substantial improvements in air quality
over time as any required controls are
installed on sources in order to meet the
State goal. For example, reductions in
NOX will contribute to visibility
improvements (69 FR June 10, 2004, at
37205–6) and will also help to reduce
acidification and eutrophication of
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8911
water bodies (69 FR January 30, 2004, at
4642–3).
2. Using State Planning Approach in
Lieu of an Increment System for NOX
a. State Planning Approach Can Meet
Requirements of Section 166 of Clean
Air Act
We believe EPA’s obligation under
section 166 to promulgate pollutantspecific regulations for NOX could be
satisfied by permitting States to
demonstrate that ‘‘other measures’’
besides increments will prevent
significant deterioration of air quality
due to NOX emissions, so long as those
measures are consistent with the
requirements of sections 166(c) and
166(d) of the Act. The EPA could satisfy
these requirements by establishing a
planning goal based on the requirements
of these provisions and then providing
a process for States to demonstrate how
the measures in their SIPs would
achieve this goal.
(1) State planning framework fulfills
many of the factors applicable under
section 166. A State planning
framework has many characteristics that
satisfy the requirements of section
166(c), and such an approach could
qualify as an ‘‘other measure’’ that is
permissible under section 166(d). A
State planning program framework, in
combination with the specific measures
in the State SIP and other Federal
measures, could fulfill the requirements
of sections 166(c) and 166(d).
Under a State planning framework, an
emissions inventory could function as a
specific numerical measure that could
be used to evaluate permit applications.
The inventory could be expressed in
terms of a mass of total emissions (tons)
across the State rather than an air
quality concentration (µg/m3) as is the
case with increments and NAAQS. The
State permitting authority could
evaluate the permit application against
the inventory of total emissions for all
sources and determine if there was room
in the inventory for a new source or an
increase in emissions from a modified
source. If so, then a preconstruction
permit could be issued without causing
emissions to exceed the level of the
inventory. If there was not room in the
inventory for emissions from a new or
modified source, then the permit
applicant would have to obtain
offsetting reductions from other sources.
This type of numerical measure could
also streamline permitting because the
evaluation of a permit application
against an emissions inventory would
be a relatively simple exercise that does
not require extensive air quality
modeling by the permit applicant.
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A State planning framework that
utilizes an emissions inventory would
also stimulate improvements in control
technology at both new and existing
sources. In order to make room in the
inventory for growth from new sources
or modifications to existing sources, a
State may elect to establish additional
control measures on existing sources.
This would stimulate improvements in
control technology at those sources.
However, a State might instead elect to
require that new and modified sources
bear a greater burden of controlling
emissions and thus stimulate these
sources to make improvements in
control technology. Major new and
modified sources would still have to
install BACT under this option, but the
State could also establish limitations
that give minor sources incentive to
employ improved control technology to
keep emissions below the inventory. A
State could also develop some
combination of these approaches that
balances the burdens across new and
existing sources. Thus, a State planning
approach of this nature would stimulate
improvements in control technology
while also providing the States with the
flexibility to identify the sources in that
State that can most cost-effectively
install improved controls.
A State planning framework could
also address the goal in section 160(4)
of the Act to assure that emissions in
one State do not interfere with the PSD
program in another State. The EPA
could adopt this goal as a criterion that
must be met in order for the State
planning process to prevent significant
deterioration of air quality due to
emissions of NOX. Thus, in addition to
showing that emissions would not
exceed the inventory, States might have
to demonstrate that their SIPs will not
cause the inventory to be exceeded in
neighboring or downwind States. The
EPA would not approve a SIP that does
not meet this goal and could thereby
ensure that emissions from upwind
States are effectively managed to
prevent significant deterioration of air
quality in other States. This goal is to a
large extent already embodied in the
State planning process based on section
110(a)(2)(D)(i)(II) of the CAA. This
section requires that SIPs contain
adequate provisions to prohibit
emissions from any source from
interfering with the part C (PSD)
program in another State. Thus, we may
not need to make any changes to our SIP
planning regulations to satisfy the
section 160(4) goal if we allowed States
to use the State planning approach to
satisfy section 166 of the Act.
With respect to the PSD goal in
section 160(5) that any decision to
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increase air pollution be made only after
careful evaluation and public
participation, the evaluation would be
conducted and opportunities for public
participation would occur under the
State’s planning approach when the
baseline year for the statewide
emissions inventory is proposed. The
EPA or the State would conduct a
careful evaluation at that time and
provide an opportunity for public
comment. Once the inventory baseline
is established, it will guide future
permit evaluations. If a project subject
to the permit requirement would not
cause statewide emissions to exceed this
level, the permit could be issued
without as extensive a review at the
permitting stage as would be required
under the increment system. The careful
evaluation conducted at the time the
baseline year is selected will have
already established whether an
emissions increase could be allowed
without preventing significant
deterioration of air quality. In addition,
major sources will still need to obtain
permits and achieve BACT, so there
would continue to be some case-by-case
review and public participation under a
State planning framework.
To satisfy the minimum requirements
of section 166(d) under the ‘‘contingent
safe harbor’’ approach, the baseline
inventory selected for a State planning
program would have to represent a level
that is at least as effective as the
increments for PM and SO2. As
discussed above, these statutory
increments were established as a
percentage of the NAAQS, which are
expressed as a concentration of air
pollution. To make a quantitative
showing that the mass-based emissions
inventory is as effective as the
concentration-based increments for PM
and SO2, EPA or the States (depending
on who establishes the inventory) could
conduct ambient air quality modeling to
predict the statewide concentrations of
NO2 achieved by maintaining the
inventory of emissions at a specific
level. The EPA or the State might then
be able to show that the selected
emissions inventory will maintain NO2
concentrations within a certain
percentage of the ambient
concentrations of NO2 as of the
applicable baseline date (or dates) in the
area. We request comment on whether
there are other equally effective
approaches (both qualitative and
quantitative) that we might use to show
that maintaining statewide emissions at
a specific level is at least as effective as
the increments for PM and SO2.
The statewide emissions level that is
as effective as the increments for PM
and SO2 would represent the ‘‘safe
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harbor’’ under the contingent safe
harbor interpretation of section 166 of
the Act. Once the safe harbor level is
identified in this manner, we would
conduct further review to determine
whether it satisfies the requirements of
section 166(c) by using the same
balancing test discussed above. We
would use this balancing test to
determine whether an emissions level
other than the ‘‘safe harbor’’ level
should be maintained to protect air
quality values, public health and
welfare, and parks and other special
areas, while also ensuring economic
growth consistent with the preservation
of existing clear air resources.
(2) A SIP that allows no increase in
total NOX emissions above 1990 levels
could satisfy section 166 requirements.
To achieve both the environmental
protection and the economic growth
goals of the PSD program in our
pollutant-specific PSD regulations for
NOX, we propose, under this State
planning option, to establish a goal that
the State maintain an emissions
inventory for NOX emissions at the
levels observed in 1990. The year 1990
is one for which we have developed
sound NOX emissions inventories for all
States as a result of our work on the
CAIR proposal. We propose the use of
this year based in part on an assumption
that the NO2 increment baseline date
(i.e., minor source baseline date) has
already been set as of that year, for all
or most of the State. Relying on this
assumption, we generally believe that
by maintaining statewide NOX emission
levels at 1990 levels, many States could
prevent significant deterioration of air
quality due to emissions from NOX and
protect AQRVs, health and welfare, and
parks and other special areas, while also
ensuring economic growth, although a
specific statewide demonstration would
still need to be submitted to EPA in
each case.
The EPA recognizes that in some
States, using a 1990 baseline inventory
for NOX may not represent a measure at
least as effective as the increments
under a SIP planning approach, even
though NOX emissions reductions are
achieved and air quality improvements
result in subsequent years when the
NO2 increment baseline concentration
date has not yet been set for all or most
areas in the State. Until the baseline
date is set for most of the State,
reductions in ambient concentrations of
NO2 would be counted as part of the
baseline concentration and would not
affect the amount of NO2 increment.
Reductions of NOX emissions in the
years following 1990 would result in
lower ambient concentrations of NO2
and thus result in a lower NO2
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increment baseline concentration.
Maintaining NOX emissions at a 1990
level when the NO2 increment baseline
had not yet been set could allow for
higher ambient NO2 concentrations than
would be allowed by adding the NO2
increment to a lower NO2 baseline
concentration. For this proposal, EPA
believes that it is necessary for the
baseline date to have already been set by
1990 in most areas of the State in order
for the State to use the 1990 NOX
inventory as its baseline NOX inventory.
While we are proposing a 1990
baseline emissions inventory date, we
believe it is possible for a State to
choose a different baseline year that
would accomplish the same objective.
Therefore, we also solicit comment on
how much flexibility States should be
given in selecting a baseline year under
this State planning option.
(3) State planning approach satisfies
ambient air quality review requirements.
If we permit States to employ a State
planning framework in lieu of NO2
increments to meet the requirements of
section 166 for NOX, we believe it will
no longer be necessary for sources to
conduct a site-specific ambient air
quality analysis for NO2 to comply with
the requirements of section 165(a)(3) of
the Act. If there is room under a
properly derived emissions inventory
for a particular new or modified source,
it will already be clear that the source
will not cause or contribute to air
pollution in excess of the NAAQS.
Before the permit is evaluated, EPA or
the State will have already performed an
ambient air quality analysis across the
State to show that holding NOX
emissions at the chosen level is
sufficient to prevent significant
deterioration of air quality or avoid an
exceedance of the NO2 NAAQS. The
statewide emissions level would fill the
role of the increment, so section
165(a)(3) would be satisfied without a
source-specific showing that a source’s
proposed emissions increase does not
cause or contribute to air pollution
increases in excess of the increment.
The permit applicant would only need
to show that there is room in the State’s
emissions inventory for its emissions.
As with the cap and trade approach
discussed above, it would become
redundant and unnecessarily costly in
many respects to require an individual
source to conduct a site-specific air
quality analysis if EPA or the State has
already established that maintaining
emissions at a specific level does not
cause air pollution to exceed standards
and meets the goals and purposes of
PSD and the requirements of section
166.
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b. Using a State Planning Approach To
Streamline the PSD Permitting Process
If a State makes the necessary
demonstration under this option, we
would not require the State to
implement some of the existing PSD
preconstruction permitting
requirements for NOX. A source-specific
ambient air quality, increment, and
NAAQS analysis would not be required,
as described in the above subsection.
However, as with the cap and trade
program option described above, we do
not propose for this State planning
approach to replace all aspects of the
PSD permitting process.
All new major stationary sources and
major modifications would still have to
obtain a permit prior to commencing
construction on new projects that result
in a significant net emissions increase
for NOX. These sources will also have to
comply with emissions limitations
based on BACT. As discussed above,
BACT is required under section
165(a)(4) of the Act, not section 166. We
do not believe this source-specific
technology requirement can be fulfilled
through alternative means under a State
planning approach.
We request comment on whether
other elements of the preconstruction
analysis would remain necessary under
this approach. If a State can maintain
NOX emissions at levels that prevent
significant deterioration of air quality,
this might also eliminate the need for
source-specific FLM review in Class I
areas. See 40 CFR 52.21(p). As
discussed above in the cap and trade
option, we propose to interpret the Act
not to require this process for NOX but
to permit EPA in its discretion to
require the process, as necessary, to
meet the requirements of section 166.
To the extent the State planning goal
protects AQRVs, this process may not be
necessary under this option for NOX.
We also request comment on whether
the additional impacts analysis (see
CAA 165(a)(6) and 40 CFR 52.21(o))
could be performed through the State
planning process and then not be
required on each individual permit
application. For the reasons discussed
above, we request comment on whether,
under this State planning option, it
would be necessary to continue to
require applicants to collect preapplication air quality monitoring data
over a 12-month period preceding the
submittal data of an application. We
believe that this kind of data may need
to be gathered by the State in order to
demonstrate that a SIP planning goal
meets the PHS requirements.
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c. What Are Some Issues That Still Need
To Be Resolved?
EPA recognizes certain significant
issues that still need to be resolved
before a comprehensive proposal can be
set forth for public review and
comment. These issues are presented
here for public consideration. The EPA
will review the comments submitted
and present its findings in a
supplemental notice in the future if the
Agency intends to continue to pursue
this option.
(1) Failure to maintain statewide
NOX emission at a level that prevents
significant deterioration of air quality.
The EPA recognizes that it may not be
possible for every State to maintain its
inventory of statewide total NOX
emissions as necessary to ensure
prevention of significant deterioration of
air quality due to emissions of NOX. For
example, this could occur where, over a
period of time, the statewide NOX
emissions from uncapped sources
substantially exceed the NOX reductions
achieved by regulating a specific group
of sources. Also, unanticipated growth
in a particular industry could cause a
State’s projection of NOX emissions for
a particular source category to be
exceeded. Consequently, in those States,
it may be difficult to demonstrate the
use of the State planning option as a
substitute for the increment system for
NOX. As stated earlier, it is the
obligation of the State to demonstrate
that the objectives of the statutory PSD
program for NOX are being met, whether
or not NOX emissions remain below the
baseline at the end of a 10-year period.
As part of the demonstration that
States must make to support the State
planning option, the State will have to
make a comprehensive showing that
total statewide NOX emissions will
continue to prevent significant
deterioration for future years. The EPA
believes that it will be necessary for the
State to conduct periodic assessments
(e.g., 10-year intervals) of NO2 air
quality trends for NOX in order to
continue justifying the SIP as a
substitute for an increment system to
prevent significant deterioration of air
quality due to emissions of NOX. The
EPA seeks comments on the frequency
of any necessary periodic assessment, as
well as other possible mechanisms for
determining when adjustments may
need to be made to a SIP that does not
employ an increment system to prevent
significant deterioration of air quality
due to emissions of NOX.
(2) Potential for localized adverse
impacts resulting from NOX emissions
increases from new and modified
sources. We recognize the possibility
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under this proposed State planning
option that sources may have
potentially adverse localized impacts
even when fulfilling statewide NOX
emissions requirements. A related
concern arises if not all source
categories are subject to the statewide
NOX emissions requirements under this
option.
Thus, while we are tentatively
considering allowing States to avoid the
need under their PSD rules to require
case-by-case source impact analyses
(including the process of involving
FLMs) under the preconstruction review
for PSD, we are at the same time
soliciting comments on how to address
the potential problem of localized
adverse impacts. We believe the
approach described under the cap and
trade option could readily apply under
the State planning option as well. That
is, regulatory procedures could be
established that would authorize the
permitting authority (or FLM, in the
case of a Class I area impact) to call for
some type of source impact analysis
when a proposed source locates within
a specified distance of an area of
concern, and the air quality in that area
has shown little or no improvement
since the State’s planning approach took
effect. We solicit comments on this and
other possible ways of addressing this
potential problem.
(3) Additional measures under a SIP.
We believe the SIP under the State
planning option will have to include
additional measures toward NOX
emissions control and/or a fall-back
increments program. A backstop for the
State planning option might involve a
margin of progress. The SIP would
contain provisions for additional
reductions or NO2 increments if the
margin of progress is exceeded. For
example, if a State’s NOX emissions rate
(tons per year) increases such that it is
within 5 percent of the baseline rate,
then the State would be obliged to
employ the additional measures in its
SIP to correct its NOX emissions. We
solicit comment on whether States
under option 3 should be required to
continue to track NO2 increment
consumption for new and modified
sources.
VII. Other Alternative Considered
As noted above, under section 166(d)
of the Act, the regulations to fulfill the
objectives of the statutory program for
PSD ‘‘may contain air quality
increments, emission density
requirements, or other measures,’’
provided such measures are at least as
effective as the increments for SO2 and
PM. Our proposed options, including
option 2 (cap and trade approach) and
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option 3 (State planning approach), are
such measures. The State planning
option gives States broad discretion in
designing their own approaches for
satisfying PSD requirements.
EPA is not proposing to utilize
‘‘critical load’’ as the basis for a
regulatory measure to prevent
significant deterioration of air quality
due to emissions of NOX at this time,
given that the science is still being
developed for the concept. The EPA
recognizes, however, that a State may
choose to utilize a critical load concept
as part of its air quality management
approach to meet its broader air quality
goals. Thus, if a State proposes to use
such a concept, considering the state of
the science and its developments over
time, to satisfy the State’s overall air
quality goals, EPA would consider it
when determining whether a State’s
approach satisfies PSD requirements.
The EPA believes that a State might
choose to pursue this concept under a
State planning option.
The National Park Service (NPS) has
been focusing on the concept of a
‘‘critical load’’ to assess the risk to park
ecosystems from atmospheric
deposition. Critical loads can be defined
as ‘‘quantitative estimates of an
exposure to one or more pollutants
below which significant harmful effects
on specified sensitive elements of the
environment do not occur according to
present knowledge’’ (1995 Staff Paper at
xi–xii). In its 1995 report entitled ‘‘Acid
Deposition Standard Feasibility Study:
Report to Congress,’’ EPA noted that
critical loads had been developed in
other countries and that, in the U.S.,
several States had developed critical
loads for acid deposition, expressed as
deposition rates for sulfur. Only in
California had critical loads been
established for nitrogen as
recommendations to protect certain
sensitive California resources (1995
Staff Paper at 53–55).
Ecosystems research over the last few
decades has produced findings that may
be sufficient to identify changes to
sensitive elements of the environment
resulting from exposure to atmospheric
nitrogen in its various forms. In some
cases, the available scientific literature
has indicated the possibility of
estimating levels of exposure at which
a particular adverse impact will result.
For exposure to nitrogen, deposition
critical load determinations are based
on indicators of harmful ecological
change that include episodic and
chronic acidification of streams and
rivers, chemical changes in soils and
vegetation, nutrient enrichment and
eutrophication, and shifts in plant
species composition. A more detailed
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description of these types of adverse
effects is contained in section V of this
preamble. Nitrogen critical load
thresholds are expressed in kilograms or
equivalents of nitrogen deposited per
hectare per year. Federal Land Managers
are beginning to evaluate the European
approach for ecosystem assessment that
uses the concept of critical loads.
Nitrogen impacts have been
documented in areas ranging from East
Coast estuaries to southern California
chaparral communities. These impacts
are found in diverse ecological
communities ranging from fisheries to
grasslands to lichens. At a given
location, different critical loads can be
developed for different ecosystem
changes (e.g., the loading at which
episodic acidification begins to occur
may be different than the loading at
which plant species shifts occur in the
same area).
As noted above, a State may wish to
identify a critical load level for nitrogen
in order to develop a ‘‘target load’’
aimed at addressing a harmful
ecosystem change, or preventing it in
places where the critical load has not
yet been reached as part of an air quality
management approach. For areas where
the critical load has already been
exceeded, a State could establish, as
part of such an approach, a target load
higher than the critical load, as a
progress goal towards the critical load.
The target load could then be used to
establish emissions goals through
deposition modeling. The State might
then choose to use efficient management
mechanisms, such as cap and trade
programs or regional emission control
strategies, to ensure that target loads are
not exceeded.
As noted above, if a State wishes to
pursue such an approach as part of its
air quality management program, the
Agency would work with the State to
determine whether the approach would
satisfy PSD requirements. In
determining whether a State’s approach
satisfies PSD requirements, EPA will
also consider other measures already
established in a State’s SIP. To the
extent a State program focused on
critical loads is needed to satisfy PSD
requirements, it would also need to be
incorporated into the SIP.
VIII. Statutory and Executive Order
Reviews
A. Executive Order 12866—Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735, October 4, 1993), the Agency
must determine whether the regulatory
action is ‘‘significant’’ and therefore
subject to review by the Office of
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Management and Budget (OMB) and the
requirements of the Executive Order.
The Order defines ‘‘significant
regulatory action’’ as one that is likely
to result in a rule that may:
(1) Have an annual effect on the economy
of $100 million or more or adversely affect
in a material way the economy, a sector of
the economy, productivity, competition, jobs,
the environment, public health or safety, or
State, local, or tribal governments or
communities;
(2) Create a serious inconsistency or
otherwise interfere with an action taken or
planned by another agency;
(3) Materially alter the budgetary impact of
entitlements, grants, user fees, or loan
programs, or the rights and obligations of
recipients thereof; or
(4) Raise novel legal or policy issues
arising out of legal mandates, the President’s
priorities, or the principles set forth in the
Executive Order.
Pursuant to the terms of Executive
Order 12866, it has been determined
that this rule is a ‘‘significant regulatory
action’’ because the cap and trade and
State planning options in the proposal
raise novel legal and policy issues. As
such, this action was submitted to OMB
for review. Changes made in response to
OMB suggestions or recommendations
will be documented in the public
record.
B. Paperwork Reduction Act
This action does not impose any new
information collection burden. Under
the proposed action, one option is to
retain the existing increments and
regulatory framework of the PSD
regulations for NOX. If the proposed
action results in our retaining the
existing increments program, the Office
of Management and Budget (OMB) has
previously approved the information
collection requirements contained in the
existing regulations (40 CFR parts 51
and 52) under the provisions of the
Paperwork Reduction Act, 44 U.S.C.
3501, et seq., and has assigned OMB
control number 2060–0003, EPA ICR
number 1230.17. A copy of the OMBapproved Information Collection
Request (ICR) may be obtained from
Susan Auby, Collection Strategies
Division, U.S. Environmental Protection
Agency (2822T), 1200 Pennsylvania
Ave., NW., Washington, DC 20460, or by
calling (202) 566–1672.
Under the second and third options of
the proposal, we are proposing to allow
States to implement alternative
programs to the NO2 increments. Option
2 would permit a State to implement a
cap and trade program. Option 3 would
permit a State to demonstrate that its
SIP requirements satisfy the objectives
of the PSD program. As presently
constructed, the proposed options do
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not impose any new information
collection burden on the States or
regulated industries. If the proposed
action results in our adopting the
second or third options, then we will be
publishing a supplemental notice and
will at that time identify any changes in
information collection requirements.
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 review instructions; 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; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and 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
control number. The OMB control
numbers for EPA’s regulations in 40
CFR are listed in 40 CFR part 9.
entities. In determining whether a rule
has a significant economic impact on
small entities, the impact of concern is
any significant adverse economic
impact on small entities, since the
primary purpose of the regulatory
flexibility analysis is to identify and
address regulatory alternatives ‘‘which
minimize any significant economic
impact of the rule on small entities.’’ 5
U.S.C. 603 and 604. Thus, an agency
may certify that a rule will not have a
significant economic impact on a
substantial number of small entities if
the rule relieves regulatory burden or
otherwise has a positive economic effect
on all of the small entities subject to the
rule. The proposed rule will not impose
any requirements on small entities and
in fact may relieve some small entities
of certain permit-related expenses.
Under option 1 of the proposal, we
would retain existing regulations
without change and thus impose no new
requirements. Under options 2 and 3 of
this proposal, we propose to allow
States to adopt alternative programs to
relieve the burden of conducting
specific ambient air quality and
increment analyses under the PSD
program. We continue to be interested
in the potential impacts of the proposed
rule on small entities and welcome
comments on issues related to such
impacts.
C. Regulatory Flexibility Act (RFA)
The Regulatory Flexibility Act (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 governmental
jurisdictions.
For purposes of assessing the impacts
of today’s proposed rule on small
entities, small entity is defined as: (1) A
small business as defined by the Small
Business Administration’s (SBA)
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; or (3) a
small organization that is any not-forprofit enterprise which is independently
owned and operated and is not
dominant in its field.
After considering the economic
impacts of today’s proposed rule on
small entities, I certify that this action
will not have a significant economic
impact on a substantial number of small
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,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for proposed and final rules
with ‘‘Federal mandates’’ that may
result in expenditures to State, local,
and tribal governments, in the aggregate,
or to the private sector, of $100 million
or more in any one year. Before
promulgating an EPA rule for which a
written statement is needed, section 205
of the UMRA generally requires EPA 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 when they are
inconsistent with applicable law.
Moreover, section 205 allows EPA to
adopt an alternative other than the least
costly, most cost-effective, or least
burdensome alternative if the
Administrator publishes with the final
rule an explanation why that alternative
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was not adopted. Before EPA establishes
any regulatory requirements that may
significantly or uniquely affect small
governments, including tribal
governments, it 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
to have meaningful and timely input in
the development of EPA regulatory
proposals with significant Federal
intergovernmental mandates, and
informing, educating, and advising
small governments on compliance with
the regulatory requirements.
Today’s action contains no Federal
mandates (under the regulatory
provisions of Title II of the UMRA) for
State, local, or tribal governments or the
private sector. The proposed rule
imposes no enforceable duty on any
State, local or tribal governments or the
private sector. Under option 1 of the
rule, we propose to retain existing
requirements and do not impose any
new Federal mandates. States are not
required to adopt the approaches set
forth in options 2 and 3 of the rule,
which may provide relief from some
existing requirements. In any event,
EPA has determined that this proposed
rule does not contain a Federal mandate
that may result in expenditures of $100
million or more for State, local, and
tribal governments, in the aggregate, or
in the private sector in any one year.
Thus, today’s proposed rule is not
subject to the requirements of sections
202 and 205 of the UMRA.
E. Executive Order 13132—Federalism
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires EPA 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, on the relationship
between the national government and
the States, or on the distribution of
power and responsibilities among the
various levels of government.’’
This proposed rule does not have
federalism implications. This proposed
rule 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. If
the existing regulations for increments
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are retained under option 1, no new
regulatory requirements will be imposed
on States. Options 2 and 3 of the
proposal would permit States to obtain
relief from certain regulatory
requirements by adopting alternative
programs but do not require adoption of
those programs. Furthermore, the cap
and trade option of this proposed rule
does not impose any requirements but
rather allows States to obtain regulatory
flexibility by implementing the
requirements of another rule. Direct
compliance costs associated with
today’s proposed rule could be incurred
when States incorporate any changes
into their State implementation plans,
but these direct compliance costs would
not be significant. Thus, Executive
Order 13132 does not apply to this
proposed rule. In the spirit of Executive
Order 13132, and consistent with EPA
policy to promote communications
between EPA and State and local
governments, EPA specifically solicits
comment on this proposed rule from
State and local officials.
F. Executive Order 13175—Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 9, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’ This proposed rule does
not have tribal implications, as specified
in Executive Order 13175. The proposed
action, whether to retain existing
regulations or to obtain regulatory
flexibility by choosing to implement an
alternative program, does not impose
any new regulatory restrictions. Thus,
Executive Order 13175 does not apply
to this proposed rule. The EPA
specifically solicits additional comment
on the proposed rule from tribal
officials.
G. Executive Order 13045—Protection of
Children From Environmental Health
and Safety Risks
Executive Order 13045, ‘‘Protection of
Children from Environmental Health
Risks and Safety Risks’’ (62 FR 19885,
April 23, 1997), applies to any rule that:
(1) Is ‘‘economically significant’’ as
defined under Executive Order 12866;
and (2) concerns an environmental
health or safety risk that EPA has reason
to believe may have a disproportionate
effect on children. If the regulatory
action meets both criteria, the Agency
must evaluate the environmental health
or safety effects of the planned rule on
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children and explain why the planned
regulation is preferable to other
potentially effective and reasonably
feasible alternatives considered by the
Agency.
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
of NOX addressed by this action present
a disproportionate risk to children.
Option 1 of the proposed rule is to
retain existing regulations and does not
impose any new regulatory
requirements. Options 2 and 3 of the
proposed rule would permit States to
obtain relief from certain regulatory
requirements by adopting alternative
programs but do not require adoption of
those programs. The public is invited to
submit or identify peer-reviewed studies
and data, of which the agency may not
be aware, that assessed results of early
life exposure to NOX.
H. Executive Order 13211—Actions
That Significantly Affect Energy Supply,
Distribution, or Use
This proposed rule is not a
‘‘significant energy action’’ as defined in
Executive Order 13211, ‘‘Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355, May
22, 2001), because it is not likely to have
a significant adverse effect on the
supply, distribution, or use of energy.
Option 1 of the proposed rule is to
retain existing regulations and does not
impose any new regulatory
requirements. Options 2 and 3 of the
proposed rule may provide relief from
certain regulatory requirements if States
adopt alternative programs. The cap and
trade option (option 2) of this proposed
rule does not impose any requirements
but rather allows States to obtain
regulatory flexibility by implementing
the requirements of another rule.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, 12(d) (15 U.S.C. 272 note),
directs EPA to use voluntary consensus
standards in its regulatory activities
unless to do so would be inconsistent
with applicable law or otherwise
impractical.
Voluntary consensus standards are
technical standards (e.g., materials
specifications, test methods, sampling
procedures, and business practices) that
are developed or adopted by voluntary
consensus standards bodies. The
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NTTAA directs EPA to provide
Congress, through OMB, explanations
when the Agency decides not to use
available and applicable voluntary
consensus standards. This proposed
rule does not involve technical
standards. Therefore, EPA is not
considering the use of any voluntary
consensus standards. The EPA
welcomes comments on this aspect of
the proposed rulemaking and
specifically invites the public to identify
potentially applicable voluntary
consensus standards and to explain why
such standards should be used in this
regulation.
List of Subjects in 40 CFR Parts 51 and
52
Environmental protection,
Administrative practices and
procedures, Air pollution control,
Intergovernmental relations, Nitrogen
oxides, Ozone, Particulate Matter,
Reporting and recordkeeping
requirements.
Dated: February 14, 2005.
Stephen L. Johnson,
Acting Administrator.
References
Allen, E.B., P.E. Padgett, A. Bytenerowicz,
R. Minnich, 1998. ‘‘Nitrogen Deposition
Effects on Coastal Sage Vegetation of
Southern California.’’ Expanded version of
presentation at the International Symposium
on Air Pollution and Climate Change Effects
on Forest Ecosystems, Riverdale, CA,
February 5–9, 1996. USDA Forest Service
Gen. Tech. Rep. Pacific Southwest Research
Station, PSW–GTR–166, p. 131–139. 1998.
Bowman, W.D., 2000. ‘‘Biotic Controls over
Ecosystem Response to Environmental
Change in Alpine Tundra of the Rocky
VerDate jul<14>2003
16:38 Feb 22, 2005
Jkt 205001
Mountains.’’ Ambio, vol. 29, no. 7 (p. 396–
400), November 2000.
Butler, T.J., G.E. Likens, and B.J.B. Stunder,
‘‘Regional-scale Impacts of Phase I of the
Clean Air Act Amendments in the USA: the
Relation Between Emissions and
Concentrations, Both Wet and Dry.’’
Atmospheric Environment, vol. 37 (p. 1015–
1028), 2000. https://www.sciencedirect.com/
science/journal/13522310.
Butler, T.J., G.E. Likens, F.M. Vermeylen,
and B.J.B. Stunder, ‘‘The Relation Between
NOx Emissions and Precipitation NO3· in
the Eastern USA.’’ Atmospheric
Environment, vol. 37 (p. 2093–2104), 2003.
https://www.sciencedirect.com/science/
journal/13522310.
Dahlgreen R.A., J.M. Holloway, ‘‘Geologic
Nitrogen as a Non-point Source of Nitrate in
Natural Waters.’’ Soil Science: Confronting
New Realities in the 21st Century (World
Congress of Soil Science); 17th WCSS, 14–21
August 2002; Symposium no. 6, paper no. 83.
https://www.sfst.org/Proceedings/
17WCSS_CD/papers/0083.pdf.
Driscoll, C.T., G.B. Lawrence, A.J. Bulger,
T.J. Butler, C.S. Cronan, C. Eagar, K.F.
Lambert, G.E. Likens, J.L. Stoddard, and K.C.
Weathers, ‘‘Acid Rain Revisited: Advances in
Scientific Understanding Since the Passage of
the 1970 and 1990 Clean Air Act
Amendments.’’ Hubbard Brook Research
Foundation Science Links’ Publication. Vol.
1, no. 1, 2001.
Fenn, M.E., M.A. Poth, J.D. Aber, J.S.
Baron, B.T. Bormann, D.W. Johnson, A.D.
Lemly, S.G. McNulty, D.F. Ryan, and R.
Stottlemyer, 1997. ‘‘Nitrogen Excess in North
American Ecosystems: Predisposing Factors,
Ecosystem Responses, and Management
Strategies.’’ Ecological Applications, vol. 8,
no. 3 (p. 706–733), August 1998.
Fenn, M.E., R. Haeuber, G.S. Tonnesen, J.S.
Baron, S. Grossman-Clarke, D. Hope, D.A.
Jaffe, S. Copeland, L. Geiser, H.M. Rueth, and
J.O. Sickman, ‘‘Nitrogen Emissions,
Deposition and Monitoring in the Western
United States.’’ BioScience, vol. 53, no. 4 (p.
1–13), April 2003.
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8917
National Oceanic and Atmospheric
Administration. (2004) AIRMon Dry
Deposition. Air Resources Laboratory. http:/
/www.arl.noaa.gov/research/
projects.airmon_dry.html; August 5, 2004.
National Science and Technology Council.
(1998) NAPAP Biennial Report to Congress:
An Integrated Assessment. National Acid
Precipitation Assessment Program. May
1998.
U.S. Department of the Interior, ‘‘Air
Quality in the National Parks: Second
Edition.’’ September 2002.
U.S. Environmental Protection Agency.
(1993) Air Quality Criteria for Oxides of
Nitrogen. (3 volumes). Office of Air Quality
Planning and Standards. EPA–600/8–91/
049aF–cF, August 1993. Available at Docket
No. AR–95–01.
U.S. Environmental Protection Agency.
(1995) Review of the National Ambient Air
Quality Standards for Nitrogen Dioxide:
Assessment of Scientific and Technical
Information. (OAQPS Staff Paper.) Office of
Air Quality Planning and Standards. EPA–
452/R–95–005, September 1995. https://
www.epa.gov/ttn/naaqs/standards/nox/
s_nox_pr_sp.html.
U.S. Environmental Protection Agency.
(1995) Acid Deposition Standard Feasibility
Study: Report to Congress. Office of Air and
Radiation. EPA 430–R–95–001a, October
1995. Available at Docket No. AR–95–01.
U.S. Environmental Protection Agency.
(1997) Nitrogen Oxides: Impacts on Public
Health and the Environment. Office of Air
Quality Planning and Standards. EPA 452/R–
97–002, August 1997.
Wang, X., ‘‘Aluminum Mobilization from
the Forest Land.’’ The Roosevelt Wild Life
Station. State University of New York;
College of Environmental Science and
Forestry. https://www.esf.edu/resorg/
rooseveltwildlife/Research/Al/Al.htm; July
28, 2004.
[FR Doc. 05–3366 Filed 2–22–05; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 70, Number 35 (Wednesday, February 23, 2005)]
[Proposed Rules]
[Pages 8880-8917]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-3366]
[[Page 8879]]
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Part II
Environmental Protection Agency
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40 CFR Parts 51 and 52
Prevention of Significant Deterioration for Nitrogen Oxides; Proposed
Rule
Federal Register / Vol. 70, No. 35 / Wednesday, February 23, 2005 /
Proposed Rules
[[Page 8880]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 51 and 52
[AD-FRL-7875-1; E-Docket ID No. OAR-2004-0013 (Legacy Docket No. A-87-
16)]
RIN-2060-AM33
Prevention of Significant Deterioration for Nitrogen Oxides
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: To preserve the air quality in national parks and other areas
that are meeting the national ambient air quality standards (NAAQS) for
nitrogen dioxide (NO2), EPA is reevaluating the increments
for NO2 that were first established in 1988 under its
program to prevent significant deterioration of air quality (PSD
program). The EPA is initiating this rulemaking action to comply with a
1990 court ruling that directed the Agency to consider and harmonize
the statutory criteria for establishing PSD regulations for nitrogen
oxides (NOX) contained in sections 166(c) and 166(d) of the
Clean Air Act (CAA or Act).
After an initial reevaluation of the existing NO2
increments under these statutory criteria, EPA is proposing three
options. One proposed option is not to change the existing increments.
We are also proposing two other options that would allow States to use
alternative approaches in lieu of the existing increments for
NO2 to satisfy the statutory criteria for preventing
significant deterioration of air quality due to emissions of
NOX. These proposed options include implementation of either
an EPA-administered cap and trade program or a State planning approach.
DATES: Comments. Comments must be received on or before April 25, 2005.
Public Hearing. If anyone contacts EPA requesting a public hearing
by March 15, 2005, we will hold a public hearing on or about March 25,
2005.
ADDRESSES: Submit your comments, identified by Docket ID No. OAR-2004-
0013, by one of the following methods:
Federal eRulemaking Portal: https://www.regulations.gov.
Follow the on-line instructions for submitting comments.
Agency Web site: https://www.epa.gov/edocket. EDOCKET,
EPA's electronic public docket and comment system, is EPA's preferred
method for receiving comments. Follow the on-line instructions for
submitting comments.
E-mail: a-and-r-docket@email.epa.gov.
Fax: (202) 566-1741.
Mail: Attention Docket ID No. OAR-2004-0013, U.S.
Environmental Protection Agency, Mailcode 6102T, 1200 Pennsylvania
Ave., NW., Washington, DC 20460. The EPA requests that a separate copy
also be sent to the contact person listed below (see FOR FURTHER
INFORMATION CONTACT).
Hand Delivery: Attention Docket Number OAR-2004-0013, U.S.
Environmental Protection Agency, EPA West (Air Docket), 1301
Constitution Ave., NW., Washington, DC 20004. Such deliveries are only
accepted during the Docket's normal hours of operation, and special
arrangements should be made for deliveries of boxed information. The
EPA requests a separate copy also be sent to the contact person listed
below (see FOR FURTHER INFORMATION CONTACT).
Instructions: Direct your comments to Docket ID No. OAR-2004-0013
(Legacy Docket No. A-87-16). The EPA's policy is that all comments
received will be included in the public docket without change and may
be made available online at https://www.epa.gov/edocket, 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
EDOCKET, regulations.gov, or e-mail. The EPA EDOCKET and the Federal
regulations.gov Web sites are ``anonymous access'' systems, 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 EDOCKET or 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, avoid any form of
encryption, and be free of any defects or viruses. For additional
information about EPA's public docket, visit EDOCKET on-line or see the
Federal Register of May 31, 2002 (67 FR 38102). For additional
instructions on submitting comments, go to section I.B of the
SUPPLEMENTARY INFORMATION section of this document.
Docket: All documents in the docket are listed in the EDOCKET index
at https://www.epa.gov/edocket. 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 EDOCKET or in hard
copy at the U.S. Environmental Protection Agency, EPA West (Air
Docket), Room B102, 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 for the Air Docket is
(202) 566-1742.
Public Hearing. People interested in presenting oral testimony or
inquiring as to whether a hearing is to be held should contact Ms.
Chandra Kennedy, OAQPS, Integrated Implementation Group, Information
Transfer and Program Integration Division (C339-03), U.S. Environmental
Protection Agency, Research Triangle Park, NC 27711, telephone number
(919) 541-5319 or e-mail kennedy.chandra@epa.gov, at least 2 days in
advance of the public hearing. People interested in attending the
public hearing must also call Ms. Kennedy 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
the proposed action. If a public hearing is held, it will be held at 10
a.m. in EPA's Auditorium in Research Triangle Park, North Carolina, or
at an alternate site nearby.
FOR FURTHER INFORMATION CONTACT: Mr. Dan deRoeck, Information Transfer
and Program Integration Division (C339-03), U.S. Environmental
Protection Agency, Research Triangle Park, NC 27711, telephone (919)
541-5593, fax (919) 541-5509, or e-mail at deroeck.dan@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Action Apply to Me?
Entities potentially affected by this proposed rule include sources
in all industry groups. The majority of sources potentially affected
are expected to be in the following groups:
[[Page 8881]]
----------------------------------------------------------------------------------------------------------------
Industry group SIC \a\ NAICS \b\
----------------------------------------------------------------------------------------------------------------
Electric Services.............................. 491 221111, 221112, 221113, 221119, 221121, 221122
Petroleum Refining............................. 291 324110
Industrial Inorganic Chemicals................. 281 325181, 325120, 325131, 325182, 211112, 325998,
331311, 325188
Industrial Organic Chemicals................... 286 325110, 325132, 325192, 325188, 325193, 325120, 325199
Miscellaneous Chemical Products................ 289 325520, 325920, 325910, 325182, 325510
Natural Gas Liquids............................ 132 211112
Natural Gas Transport.......................... 492 486210, 221210
Pulp and Paper Mills........................... 261 322110, 322121, 322122, 322130
Paper Mills.................................... 262 322121, 322122
Automobile Manufacturing....................... 371 336111, 336112, 336211, 336992, 336322, 336312,
336330, 336340, 336350, 336399, 336212, 336213
Pharmaceuticals................................ 283 325411, 325412, 325413, 325414
----------------------------------------------------------------------------------------------------------------
\a\ Standard Industrial Classification
\b\ North American Industry Classification System.
Entities potentially affected by the proposal also include States,
local permitting authorities, and Indian Tribes whose lands contain new
and modified major stationary sources.
B. What Should I Consider as I Prepare My Comments for EPA?
1. Submitting CBI
Do not submit proprietary or confidential business information
(CBI) to EPA through EDOCKET, 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. Send an
additional copy, clearly marked as CBI, as above, to: Mr. Roberto
Morales, OAQPS Document Control Officer (C339-03), U.S. Environmental
Protection Agency, Research Triangle Park, NC 27711.
2. Tips for Preparing Your Comments
When submitting comments, remember to:
i. Identify the rulemaking by docket number and other identifying
information (e.g., subject heading, Federal Register proposal
publication date and reference page number(s)).
ii. 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.
iii. Explain why you agree or disagree; suggest alternatives and
provide substitute language for your requested changes.
iv. Describe any assumptions and provide any technical information
and/or data that you used.
v. If you estimate potential costs or burdens, explain how you
arrived at your estimate in sufficient detail to allow for it to be
reproduced.
vi. Provide specific examples to illustrate your concerns, and
suggest alternatives.
vii. Explain your views as clearly as possible, avoiding the use of
profanity or personal threats.
viii. Make sure to submit your comments by the comment period
deadline identified.
C. Where Can I Obtain Additional Information?
In addition to being available in the docket, an electronic copy of
today's proposed rule is also available on the World Wide Web through
the Technology Transfer Network (TTN). Following signature by the EPA
Administrator, a copy of today's proposed rule will be posted on the
TTN's policy and guidance page for newly proposed or promulgated rules
at https://www.epa.gov/ttn/oarpg. The TTN provides information and
technology exchange in various areas of air pollution control. If more
information regarding the TTN is needed, call the TTN HELP line at
(919) 541-5384.
D. How Is this Preamble Organized?
The information presented in this preamble is organized as follows:
I. General Information
A. Does This Action Apply To Me?
B. What Should I Consider as I Prepare My Comments for EPA?
C. Where Can I Obtain Additional Information?
D. How Is This Preamble Organized?
II. Overview of Today's Proposed Action
A. Option 1: Retain Existing Increment System for NOX
B. Option 2: Allow States To Use a Cap and Trade Program in Lieu
of an Increment System for NOX
C. Option 3: Allow States Flexibility To Use a State Planning
Approach in Lieu of an Increment System for NOX
III. Background
A. PSD Program
B. Existing Section 166 Regulations for NOX
1. Statutory Provisions
2. The 1988 NO2 Increments
C. Court Decision
IV. Legal Authority
A. Interpretation on Remand: Harmonizing Sections 166(c) and
166(d) of the Clean Air Act
B. Interpretation on Remand: The Section 166(c) Factors
1. Numerical Measures by Which Permit Application May Be
Evaluated
2. Protect Air Quality Values
3. Protect Public Health and Welfare From Adverse Effects
Notwithstanding Attainment of NAAQS
4. Ensure Economic Growth Consistent With Preservation of
Existing Clean Air Resources
[[Page 8882]]
C. EPA's Authority To Fulfill Section 166 Requirements by
Granting States Flexibility To Adopt Alternative Measures in Their
SIPs
V. Health and Welfare Effects of NOX
A. Scope of Effects EPA Proposes To Consider
B. Data Included in Review
C. Analysis of Effects
1. Health Effects
2. Welfare Effects
VI. Proposed Actions
A. Retain Existing Increment System for NOX
1. How Existing Characteristics of the Regulatory Scheme Fulfill
Statutory Criteria
2. Proposed Actions Regarding Characteristics of NO2
Increments
B. Regional Cap and Trade Program
1. Description of Cap and Trade Programs
2. Using a Cap and Trade Program in Lieu of an Increment System
for NOX
C. State Planning Approach
1. Description of State Planning Approach
2. Using State Planning Approach in Lieu of an Increment System
for NOX
VII. Other Alternative Considered
VIII. 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. Overview of Today's Proposed Action
To ensure protection of the air quality in national parks and other
areas that meet the NAAQS for NO2, EPA is reevaluating the
NO2 increments that were first established in 1988 under the
PSD program. In accordance with the directions of a 1990 court ruling,
the Agency is conducting this review to consider and harmonize the
statutory criteria, contained in subsections 166(c) and 166(d) of the
Act, that govern the content of EPA's pollutant-specific PSD
regulations for NOX. The EPA is proposing to apply these
criteria using the ``contingent safe harbor'' approach that was
suggested by the court as an appropriate way to ensure that EPA's PSD
regulations for nitrogen oxides will prevent significant deterioration
of air quality due to emissions of NOX in parks and other
areas that are either designated to be in attainment with the NAAQS or
are unclassifiable.
Today's proposal includes three options to address our
responsibility to promulgate pollutant-specific regulations to prevent
significant deterioration of air quality from emissions of
NOX and to preserve, protect and enhance the air quality in
our national parks and other areas of special interest. The first
option is to retain the existing regulatory format using the increments
that we originally adopted in 1988. We also propose two alternative
approaches that we believe would satisfy the goals and objectives of
the statutory PSD program in lieu of the existing NO2
increments. These two additional options, for which we are seeking
public comment today, would permit States to adopt a specific market-
based cap and trade approach or to demonstrate that strategies and
measures in their State Implementation Plans (SIPs), in conjunction
with other Federal requirements, will prevent significant deterioration
of air quality due to emissions of NOX. Each of these
options is summarized immediately below and described in greater detail
in section VI of this preamble.
A. Option 1: Retain Existing Increment System for NOX
The EPA is reviewing whether, considering the criteria in section
166(c), EPA should establish different increments for NOX
than the ones that were adopted in 1988. The existing increments were
established as a percentage of the NAAQS, and were based on the ambient
measure (NO2) and the same time period (annual) as the
NAAQS. An increment with these characteristics satisfies the minimum
requirements of section 166(d) of the Act for preserving the air
quality in parks and other attainment and unclassifiable areas. In
accordance with the ``contingent safe harbor'' approach, EPA is
undertaking this additional review to determine whether the criteria in
section 166(c) indicate that it is necessary for EPA to deviate from
this ``safe harbor'' in order to satisfy the criteria in section
166(c).
Based on our initial review of the existing NO2
increments under these statutory criteria, one option is to retain the
existing PSD regulations for NOX, which includes the
existing NO2 increments, without modification because we
believe the existing regulations protect the air quality in national
parks and other attainment or unclassifiable areas, within the context
of the criteria of section 166(c). Our review has considered and
balanced the criteria in section 166(c) and the incorporated goals and
purposes of the PSD program set forth in section 160 of the Act. We
have also reviewed the existing regulatory framework of the Agency's
PSD regulations for NOX and the scientific and technical
information pertaining to the health, welfare, and ecological effects
of NOX. In light of this review, EPA believes that the
statutory requirements are met by retaining annual NO2
increments based on the percentages of the NAAQS employed to set the
increments for sulfur dioxide (SO2). The available research
on health and welfare effects indicates that the existing increments,
in conjunction with the case-by-case permit review for additional
impacts and impairment of air quality related values (AQRV), fulfills
the criteria in section 166(c). The EPA requests comment on this option
and its supporting review.
B. Option 2: Allow States To Use a Cap and Trade Program in Lieu of an
Increment System for NOX
As an alternative approach to retaining the existing increment
system for NOX, we are soliciting comments on a proposed
option that would allow States to prevent significant deterioration of
air quality due to emissions of NOX by implementing the
model cap and trade program for EGUs contained in our proposed Clean
Air Interstate Rule (CAIR).\1\ A State that implements this program to
address NOX emissions would no longer be required to conduct
certain source-specific analyses, including the current NO2
increment analysis.
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\1\ EPA proposed the CAIR, originally called the Interstate Air
Quality Rule (IAQR), on January 30, 2004 (69 FR 4566), followed by a
supplemental notice of proposed rulemaking on June 10, 2004 (69 FR
32684), to reduce emissions of SO2 and NOX in
29 States and the District of Columbia to contribute to the
attainment of the PM2.5 and 8-hour ozone NAAQS in a
number of eastern States.
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This option would require States to revise their SIPs to include a
cap and trade program to reduce NOX emissions in accordance
with statewide emissions budgets prescribed by EPA. Neither the
statewide budget nor the regional cap would be a legally enforceable
limit on total NOX emissions but would be used as an
accounting technique to determine the amount of emissions reductions
that would be needed from specific source categories to satisfy the
budget or cap. The requirements of the cap and trade program would be
enforceable, and this would ensure that as long as emissions from
sources outside of the cap did not grow more than projected, the
overall regionwide budget would be met.
As described in greater detail in section VI.B of this preamble, we
believe that such a cap and trade program, while designed to address
other CAA program requirements, is also an effective alternative to
[[Page 8883]]
increments for preventing significant deterioration from emissions of
NOX. The EPA has utilized this approach with considerable
success in several instances. The EPA proposed a model multi-State cap
and trade program in its June 10, 2004, supplemental notice for the
CAIR proposal that States could choose to adopt to meet the proposed
emissions reductions requirements in a flexible and cost-effective
manner. The EPA believes that the implementation of this kind of cap
and trade program could bring about significant improvements in air
quality and would offer many advantages over traditional command-and-
control and project-by-project emissions reduction credit trading
programs.
C. Option 3: Allow States Flexibility To Use a State Planning Approach
in Lieu of an Increment System for NOX
As a third option, we propose to allow a State to forego
implementation of the NO2 increments and associated
requirements if the State can demonstrate that measures in its SIP, in
conjunction with Federal requirements, would prevent significant
deterioration of air quality from emissions of NOX. In lieu
of implementing the increment system for NOX, a State would
have to demonstrate that the specific planning goals and requirements
contained in its SIP would satisfy the requirements in section 166 of
the Act and the goals and purposes of the PSD program set forth in
section 160.
This option would provide States with the flexibility to design a
program to prevent significant deterioration of air quality from
emissions of NOX that may be more effective than increments.
States would have to establish a clear planning goal that satisfies the
requirements of sections 166(c) and 166(d) of the Act. To achieve this
goal, a State could impose NOX emissions limitations on any
type of emissions sources it chooses, including new or existing
sources. Under this option, EPA does not propose to require a State to
demonstrate that its SIP includes a specific type of program that we
believe is sufficient to satisfy the requirements of section 166.
However, we believe that a goal to keep statewide emissions of
NOX from all sources below 1990 levels would prevent
significant deterioration of air quality and satisfy the requirements
of section 166 of the Act. Adoption of this goal could streamline our
review of the State's demonstration, but a State would not be precluded
from using another approach to prevent significant deterioration of air
quality due to emissions of NOX.
III. Background
A. PSD Program
Part C of title I of the Act contains the requirements for a
component of the major new source review (NSR) program known as the
Prevention of Significant Deterioration (PSD) program. This program
sets forth procedures for the preconstruction review and permitting of
new and modified major stationary sources of air pollution locating in
areas meeting the NAAQS (``attainment'' areas) or areas for which there
is insufficient information to classify an area as either attainment or
nonattainment (``unclassifiable'' areas).
The applicability of the PSD program to a particular source must be
determined in advance of construction and is pollutant specific. For
new sources locating in an attainment or unclassifiable area, PSD
applies when the source qualifies as a major source because it has the
potential to emit any regulated NSR pollutant equals or exceeds either
100 or 250 tons per year (tpy) depending on the source category. In
addition to reviewing the pollutant emitted at or in excess of the
``major source'' levels, the PSD permit review also covers each
regulated NSR pollutant for which the area is in attainment or
unclassifiable that the source would have the potential to emit in
significant amounts.
For modified sources, PSD applies when an existing major stationary
source undergoes a nonexcluded physical change or change in the method
of operation that results in a significant net emissions increase of
any regulated NSR pollutant for which the area is in attainment or
unclassifiable. The PSD regulations define ``significant'' as a
specific emissions rate (tons per year) for each regulated pollutant.
Each regulated NSR pollutant emitted by the source must be reviewed
independently for applicability purposes. Moreover, to determine the
emissions of a particular pollutant for applicability purposes, the
source may take into account the use of emissions control technology
and restrictions on the hours of operation or rates of production,
where such controls and restrictions are enforceable.\2\
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\2\ On December 31, 2002, we revised the PSD regulations to,
among other things, enable major sources undergoing modification of
existing emissions units to project future emissions increases on
the basis of projected utilization of the modified equipment. Most
States have not yet adopted the new provisions but they are in
effect in States where EPA is the permitting authority (i.e., where
no State PSD rule has been approved by EPA) or where the State PSD
rule incorporates the Federal regulations by reference. 67 FR 80186;
68 FR 11316 (March 10, 2003).
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Once a source is determined to be subject to PSD, it must undertake
a series of analyses to demonstrate that it will use the best available
control technology (BACT) and will not cause or contribute to a
violation of any NAAQS or incremental ambient pollutant concentration
increase. In cases where the source's emissions may adversely affect an
area classified as a Class I area, additional review is conducted to
protect the increments and special attributes of such an area defined
as ``air quality related values.''
When the permitting authority reaches a preliminary decision to
authorize construction of each proposed major new source or major
modification, it must provide notice of the preliminary decision and an
opportunity for comment by the general public, industry, and other
persons that may be affected by the major source or major modification.
After considering and responding to the comments, the permitting
authority may issue a final determination on the construction permit in
accordance with the PSD regulations.
B. Existing Section 166 Regulations for NOX
1. Statutory Provisions
In section 166(a) of the Act, Congress directed EPA to conduct a
study and promulgate regulations to prevent significant deterioration
of air quality which would result from emission of hydrocarbons, carbon
monoxide, photochemical oxidants, and NOX. Congress further
specified that such regulations meet the following requirements set
forth in sections 166(c) and 166(d):
(c) Such regulations shall provide specific numerical measures
against which permit applications may be evaluated, a framework for
stimulating improved control technology, protection of air quality
values, and fulfill the goals and purposes set forth in section 101
and section 160.
(d) The regulations * * * shall provide specific measures at
least as effective as the increments established in section 163 [for
SO2 and PM] to fulfill such goals and purposes, and may
contain air quality increments, emission density requirements, or
other measures.
The goals and purposes of the PSD program set forth in section 160
are as follows:
(1) to protect public health and welfare from any actual or
potential adverse effect which in the Administrator's judgment may
reasonably be anticipate[d] to occur from air pollution or from
exposures to pollutants in other media, which pollutants originate
as emissions to the ambient air, notwithstanding attainment and
maintenance of all national ambient air quality standards;
[[Page 8884]]
(2) to preserve, protect, and enhance the air quality in
national parks, national wilderness areas, national monuments,
national seashores, and other areas of special national or regional
natural, recreational, scenic, or historic value;
(3) to insure that economic growth will occur in a manner
consistent with the preservation of existing clean air resources;
(4) to assure that emissions from any source in any State will
not interfere with any portion of the applicable implementation plan
to prevent significant deterioration of air quality for any other
State; and
(5) to assure that any decision to permit increased air
pollution in any area to which this section applies is made only
after careful evaluation of all the consequences of such a decision
and after adequate procedural opportunities for informed public
participation in the decisionmaking process.
Furthermore, the goals and purposes of the CAA set forth in section
101 are as follows:
(b) * * * (1) to protect and enhance the quality of the Nation's
air resources so as to promote the public health and welfare and the
productive capacity of its population;
(2) to initiate and accelerate a national research and
development program to achieve the prevention and control of air
pollution;
(3) to provide technical and financial assistance to State and
local governments in connection with the development and execution
of their air pollution prevention and control programs; and
(4) to encourage and assist the development and operation of
regional air pollution prevention and control programs [; and]
(c) * * * to encourage or otherwise promote reasonable Federal,
State, and local governmental actions, consistent with the
provisions of this Act, for pollution prevention.
2. The 1988 NO2 Increments
On October 17, 1988, EPA promulgated pollutant-specific PSD
regulations for NOX under section 166 of the CAA. 53 FR
40656. The EPA decided to establish NO2 increments following
the pattern enacted by Congress for the PM and SO2
increments. These increments establish maximum increases in ambient air
concentrations of NO2 (expressed in micrograms per cubic
meter ([mu]g/m3)) allowed in a PSD area over a baseline
concentration. Emissions increases from both stationary and mobile
sources are considered in the consumption of the NO2
increments which are implemented through the PSD permitting provisions
in 40 CFR parts 51 and 52.
The increment system for NOX includes the three-tiered
area classification system established by Congress in section 163 for
increments of SO2 and PM. Class I areas (including certain
national parks and wilderness areas) were designated by Congress as
areas of special national concern, where the need to prevent air
quality deterioration is the greatest. Consequently, the allowable
level of incremental change in air quality is most stringent in Class I
areas. Class II areas are all areas not specifically designated in the
Act as Class I areas. The increments of Class II areas are less
stringent than the Class I areas and allow for a moderate degree of
emissions growth. Class III areas are areas originally designated as
Class II, that have been redesignated by States where higher levels of
industrial development (and emissions growth) are desired, and are
allowed to have the greatest increase in ambient concentration. There
have been no Class III redesignations to date.
EPA based the levels of the increments for each area classification
on the percentages of the NAAQS that Congress used to set the
increments for SO2 and PM. Congress used different
percentages of the NAAQS to calculate the Class I increments for PM and
SO2. For the NO2 increments, we chose the
percentage that Congress used for SO2. This decision yielded
a lower Class I increment for NO2 than would have resulted
by using the PM percentage.
The existing Class I NO2 increment is 2.5 [mu]g/
m3 (annual average), a level of 2.5 percent of the
NO2 NAAQS. It is based on the Class I SO2
increment, which is set at the same percentage (2.5 percent) of the
SO2 annual NAAQS. The Class II NO2 increment is
25 [mu]g/m3-25 percent of the NO2 NAAQS. The
Class III NO2 increment is 50 [mu]g/m3-50 percent
of the NO2 NAAQS.
EPA believed that these increments satisfied the standard in
section 166(d), which requires that PSD regulations for NOX
be ``at least as effective'' as the existing section 163 increments in
preventing significant deterioration of air quality due to emissions of
NOX. The EPA thought that reflecting the same percentages of
the NAAQS as the SO2 and PM increments would be at least as
stringent as the statutorily established increments in terms of ambient
air quality impacts. In the preamble to these regulations, EPA
explained that the increments satisfied the section 166(c) criteria by
providing numerical measures against which permit applications may be
evaluated and stimulating improved control technology. The EPA relied
on the establishment of a Class I NO2 increment and the
provisions for protecting AQRVs in section 165(d)(2) (providing a role
for the Federal Land Manager (FLM) in the review of certain PSD permits
prior to issuance) to protect air quality values affected by
NOX. The EPA further reasoned that these ambient
concentration percentages could be used as a proxy for all the PSD
purposes set forth in the statute, thus satisfying the ``goals and
purposes set forth in section 101 and section 160'' incorporated by
reference in section 166(c).
C. Court Decision
In 1988, the Environmental Defense Fund (now Environmental Defense,
or ``ED'') filed suit in the U.S. Court of Appeals for the District of
Columbia Circuit against the Administrator (Environmental Defense Fund,
Inc. v. Reilly, No. 88-1882). ED argued that EPA failed to sufficiently
consider several of the section 166(c) criteria. ED also argued that
EPA's approach failed to satisfy the ``at least as effective'' standard
under section 166(d) because EPA did not compare the NO2
increments (set only for the annual averaging period) to the 24-hour
and 3-hour increments for SO2.
In its 1990 opinion, the court held that EPA had satisfied its
obligation under section 166(d) but had not sufficiently considered
whether different increments should be established under the criteria
in section 166(c). More specifically, the court held that EPA's
percentage-of-NAAQS approach for determining the increments satisfied
the duty under section 166(d) to promulgate regulations for
NOX that were ``at least as effective'' as the increments in
section 163. Id. at 188. As to subsection (c), however, the court held
that EPA's approach of using the percentage ambient concentrations as a
``proxy'' for meeting the subsection (c) criteria overlooked the
language of subsection (c), and turned subsection (c) into an option,
despite its mandatory wording. Thus, the court remanded the case to EPA
``to develop an interpretation of section 166 that considers both
subsections (c) and (d), and if necessary to take new evidence and
modify the regulations.'' Environmental Defense Fund v. EPA, 898 F.2d
183, 190 (DC Cir. 1990) (``EDF v. EPA'').
The court identified three steps that EPA took to develop PSD
regulations for NOX under section 166. The first two steps
reflected EPA's decisions to adopt regulations for NOX that
employed increments with an area classification system to implement the
PSD program for NOX. These first two steps were not
controverted in EDF v. EPA, 898 F.2d at 184-85. The dispute in the EDF
case involved only the third step, which was EPA's action to establish
several characteristics of the increments by reference to the NAAQS.
The
[[Page 8885]]
characteristics that EPA derived from the NAAQS were (1) the level of
the increments using the percent-of-NAAQS-approach; (2) the time period
(annual average) for the increments; and (3) the pollutant
(NO2) for which the increments were established. Since these
three characteristics of the increments were the only issues
controverted in the EDF v. EPA case, EPA is revisiting only these
questions to satisfy the court's remand. However, we also believe it
would be beneficial to consider alternative approaches to an increment
system and thus are voluntarily reconsidering the first two steps in
the process of developing pollutant-specific PSD regulations for
NOX.
In EDF v. EPA, the court held that, in light of the criteria in
section 166(c), EPA could not use the NAAQS as the sole basis for
deriving increments. However, the court held that using the NAAQS as
the basis for deriving increments was permissible in determining
whether the ``at least as effective'' standard under subsection (d) was
met. But, with respect to subsection (c), the court stated: ``we find
nothing in the language or legislative history suggesting that this
duty [consideration of the goals and purposes of the statute] could be
satisfied simply by referencing the NAAQS.'' Id. at 190. The court
noted the differences between the health and welfare criteria on which
the NAAQS are based (sections 108 and 109) and the ``goals and
purposes'' of the PSD program set forth in section 160, highlighting
the special value the PSD program places on protection of national
parks. At the same time, the court recognized that ``[n]evertheless,
the ambient standards are the basic measure of air quality under the
[Clean Air Act], and the controlling standards by no means exclude any
value that is the subject of focus under the PSD provisions.'' Id. at
176 (internal citations and quotations omitted). In other words, the
court observed that NAAQS remain relevant to the inquiry under section
166 because they are a basic measure of air quality and may indirectly
reflect some consideration, among others, of the same values that are
the focus of the PSD program. However, the court indicated that we
could not rely solely upon the NAAQS to comply with section 166 because
this provision directs us to focus on the specific goals and purposes
of PSD which are not necessarily the factors that determine the NAAQS
under section 109.
Thus, the court directed EPA to reconsider the characteristics of
the existing increments in light of the criteria in both sections
166(c) and 166(d). The court indicated that one permissible
interpretation for harmonizing subsections (c) and (d) would be to
construe subsection (d) as a ``contingent safe harbor'' or presumptive
baseline. Thus, increments derived from the NAAQS could be authorized
if the agency were to undertake additional analysis and make a reasoned
determination that the criteria under subsection (c) do not call for
different increments than the ``safe harbor'' that meets the criteria
in subsection (d) of the statute.
On July 31, 2003, Environmental Defense (ED) petitioned the court
to order EPA to take action in accordance with the court's earlier
opinion. ED and EPA reached a settlement in which EPA agreed to propose
and promulgate a rule to fully comply with the court's remand order.
The settlement obligated the Agency to issue a proposal no later than
September 30, 2004, and a final rule no later than September 30, 2005.
However, in September 2004, EPA and ED agreed to extend the proposal
deadline until February 14, 2005 in order to allow EPA more time to
consider alternatives to the increment approach.
IV. Legal Authority
Section 166(a) of the Act directs EPA to develop pollutant-specific
regulations to prevent the significant deterioration of air quality.
Sections 166(c) and 166(d) of the Act provide more detail on the
contents of those regulations. To develop pollutant-specific
regulations under subsection (a), EPA must establish an overall
regulatory framework for those regulations and fill in many specific
details around that framework.
EPA interprets section 166 to require that its PSD regulations for
a particular pollutant must, as a whole, satisfy the criteria in
section 166. Thus, we believe our obligations under section 166(c) of
the Act are satisfied when the entire body of pollutant-specific
regulations for NOX (including the overall regulatory
framework and the specific details) satisfy the criteria in sections
166(c) and 166(d) of the Act.
In the case of NOX, EPA established that overall
framework in the 1988 rulemaking and employed NO2 increments
and an area classification system for these regulations.\3\ This
increment system for NOX was modeled on the system that
Congress had already established for PM and SO2. Within this
overall system, EPA then filled in specific details, including defining
the characteristics of the increments to be developed for
NOX.
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\3\ Under section 166(e) of the Act, a State is authorized to
develop measures to prevent significant deterioration of air quality
other than an area classification scheme for pollutants other than
PM and SO2 if the implementation plan contains other
provisions that the Administrator finds will ``carry out the
purposes in section 160 at least as effectively as an area
classification plan for such pollutant.''
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The dispute in EDF v. EPA involved only EPA's decisions to define
the characteristics of the increments for NOX in relation to
the NAAQS. Since the basic increments and area classification system in
EPA's PSD regulations for NOX were not controverted, EPA
does not interpret the court's opinion to require that the Agency
reconsider these fundamental aspects of its PSD regulations for
NOX. Thus, EPA believes that it is only required at this
time to reconsider the level, time period, and pollutant used in
establishing increments in its PSD regulations for NOX.
However, EPA is also requesting comment in this proposed rule on
alternatives to the current increment system for NOX. Based
on the input from various stakeholders, EPA is voluntarily
reconsidering whether the increment system is the most effective
mechanism for fulfilling our obligations to protect parks and other
attainment areas under section 166 of the Act. Thus, as alternatives to
our proposing to retain the existing increment system for
NOX, we are also proposing to allow the States to implement
an EPA-administered cap and trade program or a State planning approach
to fulfill our obligation to establish pollutant-specific PSD
regulations for NOX.
A. Interpretation on Remand: Harmonizing Sections 166(c) and 166(d) of
the Clean Air Act
We propose to harmonize the criteria set forth in sections 166(c)
and 166(d) by using the ``contingent safe harbor'' approach discussed
by the Court. We believe this is an appropriate reading of the statute.
Subsection (c) describes the kinds of measures to be contained in the
regulations to prevent significant deterioration of air quality called
for in section 166(a) and specifies that these regulations are to
``fulfill the goals and purposes'' set forth in sections 160 and 101 of
the Act. Then, under subsection (d), to ``fulfill such goals and
purposes,'' EPA must promulgate ``specific measures at least as
effective as the increments established in section 7473 of this title
[section 163 of the Act].'' 42 U.S.C. 7476. Subsection (d) indicates
that these specific measures may include increments but are not
necessarily required to contain increments. Thus, subsection (d) can be
construed to require that EPA identify a minimum level of
effectiveness, or safe
[[Page 8886]]
harbor, for the body of pollutant-specific PSD regulations adopted
under section 166. Then, subsection (c) may be read to require that EPA
conduct further review to determine whether, based on the criteria in
subsection (c), EPA's pollutant-specific PSD regulations under section
166 should contain measures that deviate from the minimum ``safe
harbor'' identified under subsection (d). As in 1988, we construe
subsection (d) to require that the measures be ``at least as
stringent'' as the statutory increments set forth in section 163.
In an instance where EPA opts to employ increments in its section
166 PSD regulations for a specific pollutant, we interpret this
language to require that EPA, at minimum, establish increments that are
consistent with the statutory increments established by Congress in
that each increment (Class I, II, or III) is established in relation to
the NAAQS and is set (1) at an equivalent percentage of the NAAQS as
the statutory increments; (2) for the same pollutants as the NAAQS; and
(3) for the same time period as the NAAQS. Under an increment approach,
EPA would then conduct further review to determine whether the ``safe
harbor'' increments, in conjunction with other measures adopted under
the PSD program and section 166, sufficiently fulfill the criteria in
subsection (c). If, after weighing and balancing the criteria set forth
in subsection (c) (and the incorporated goals and purposes of the CAA
in section 101 and the PSD program in section 160), EPA determines that
the ``safe harbor'' increments and other measures do not satisfy these
criteria, then EPA would need to develop additional regulations which
may include different increments, additional increments, or additional
measures to satisfy the section 166(c) criteria. If EPA determines that
the ``safe harbor'' increments and associated measures satisfy the
criteria in subsection (c), then it need not adopt different or
additional increments or other measures as part of its PSD regulations
under section 166.
B. Interpretation on Remand: The Section 166(c) Factors
EPA interprets section 166(c) of the Act to establish eight factors
to be considered in the development of PSD regulations for the
pollutants covered by this provision. Section 166(c) lists three
specific criteria that EPA must consider in the development of PSD
regulations for the pollutants covered by this provision. These three
criteria indicate that PSD regulations for specific pollutants should
provide (1) specific numerical measures for evaluating permit
applications; (2) a framework for stimulating improved control
technology; and (3) protection of air quality values. 42 U.S.C.
7476(c). In addition, section 166(c) directs that EPA's PSD regulations
for specific pollutants ``fulfill the goals and purposes'' set forth in
sections 101 and 160 of the Act. 42 U.S.C. 7476(c). We interpret this
phrase to incorporate the five goals and purposes of the PSD program
set forth in section 160 as factors that EPA must consider to comply
with section 166(c) of the Act.
The Agency's view is that PSD measures that satisfy the specific
goals and purposes of section 160 also satisfy the more general
purposes and goals identified in section 101 of the Act. The overall
goals and purposes of the CAA listed in sections 101(b) and 101(c) are
general goals regarding protecting and enhancing the nation's air
resources and controlling and preventing pollution. Because these broad
goals are given more specific meaning in section 160, EPA does not
believe it is necessary to consider them in detail when evaluating
whether PSD regulations satisfy the criteria in section 166(c). In
addition, the court's inquiry in EDF v. EPA focused exclusively on the
specific goals and purposes of the PSD program set forth in section
160. However, because the broad purpose of the CAA set forth in section
101(b)(1) provides some additional guidance as to the meaning of the
more specific PSD goal set forth in section 160(3), we discuss section
101(b)(1) further below in this limited context of interpreting one of
the factors applicable under section 166.
Thus, EPA construes the term ``fulfill the goals and purposes,'' as
used in section 166(c), to mean that EPA should apply the goals and
purposes listed in section 160 as factors applicable to pollutant-
specific PSD regulations established under section 166. The EPA's PSD
regulations for NOX should therefore be consistent with the
three criteria listed in section 166(c) and the five goals and purposes
listed in section 160 of the Act.
As noted above and explained further below, for the increment
option in this proposal, we believe many of the eight factors
applicable under section 166(c) are fulfilled by elements of the
regulatory framework that were established in 1988 and not controverted
in EDF v. EPA. We discuss further below how the proposed cap and trade
and State planning options also satisfy these factors. The following
sections provide more detail on how we propose to interpret and apply
several of these factors in developing pollutant-specific PSD
regulations under section 166 of the Act.
1. Numerical Measures by Which Permit Application May Be Evaluated
The first criterion in section 166(c) states that pollutant-
specific PSD regulations must contain ``specific numerical measures
against which permit applications may be evaluated.'' We believe an
increment would clearly satisfy this criterion but do not interpret
section 166 to require that we employ an increment system for every
pollutant listed in this section. Section 166(d) states that our
pollutant-specific PSD regulations ``may contain'' increments or
``other measures.'' We interpret this provision to allow EPA or the
States to employ approaches other than an increment system, so long as
such an approach fulfills the ``specific numerical measures'' criterion
in section 166(c).
While an increment is the clearest example of a specific numerical
measure for evaluating permit applications because of the model
Congress established for PM and SO2, the Act gives EPA the
discretion to employ other types of numerical measures in PSD
regulations for the other pollutants listed in section 166, such as
``nitrogen oxides.'' An increment represents the allowable marginal
increase in air pollutant concentration (measured in [mu]g/m\3\. Under
this approach, the permit applicant must conduct modeling to determine
whether or not its emissions on a mass basis (e.g., tons) will result
in an air quality concentration increase in excess of the increment.
However, another way to provide a numerical measure for evaluating
permits could be, for instance, to establish a maximum allowable level
of emissions on a mass basis (e.g., tons).
Under the latter approach, permit applicants would have to show
that their emissions will not cause total emissions in a given area to
exceed the maximum allowable level of emissions established for that
area. Under a State planning approach, the State could monitor the
inventory of emissions from all sources (new and existing) and only
issue a permit if the applicant's project would not cause emissions to
exceed allowable levels. Using a cap and trade approach, EPA or the
States could adopt regional or statewide caps on emissions of specific
sources that could then be allocated to States or individual sources
covered by the cap in the form of a budget or allowance. Individual
permit applications would be evaluated against the cap by determining
whether the applicant held a sufficient number of allowances.
[[Page 8887]]
2. Protect Air Quality Values
The third criterion in section 166(c) broadly states that the
regulations ``shall provide * * * protection of air quality values''
without identifying the air quality values to be protected. Legislative
history indicates that the term ``air quality value'' was used
interchangeably with the term ``air quality related value'' (AQRV)
regarding Class I lands.\4\ Thus, we believe the term ``air quality
values'' should be given the same meaning as ``air quality related
values.''
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\4\ See S. Rep. 95-127, at 12, reprinted at 3 Legislative
History at 1386, 1410 (describing the goal of protecting ``air
quality values'' in ``Federal lands--such as national parks and
wilderness areas and international parks,'' and in the next
paragraph and subsequent text using the term ``air quality related
values'' to describe the same goal); id. at 35, 36 (``The bill
charges the Federal land manager and the supervisor with a positive
role to protect air quality values associated with the land areas
under the jurisdiction of the [FLM]'' and then describing the
statutory term as ``air quality related values''). H.R. Report 95-
564 at 532 (describing duty of Administrator to consider ``air
quality values'' of the tribal and State lands in resolving an
appeal of a tribal or State redesignation, which is described in the
final bill as ``air quality related values'').
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The Act does not define AQRV, except to note that it includes
visibility. Section 165(d)(1)(B). However, the legislative history
provides the following explanation of AQRV:
The term ``air quality related values'' of Federal lands
designated as class I includes the fundamental purposes for which
such lands have been established and preserved by the Congress and
the responsible Federal agency. For example, under the 1916 Organic
Act to establish the National Park Service (16 U.S.C. 1), the
purpose of such national park lands ``is to conserve the scenery and
the natural and historic objects and the wildlife therein and to
provide for the enjoyment of the same in such manner and by such
means as will leave them unimpaired for the enjoyment of future
generations.''
S. Rep. 95-127 at 36, reprinted at 3 Legislative History at 1410.
Thus, in 1996, the Agency proposed the following definition of
AQRV:
* * * visibility or a scenic, cultural, physical, biological,
ecological, or recreational resource that may be affected by a
change in air quality, as defined by the Federal Land Manager for
Federal lands, or by the applicable State or Indian Governing Body
for nonfederal lands.
61 FR 38250, 38322 (July 23, 1996). The reference to State or Indian
Governing Body was to acknowledge that Congress recognized in section
164(e) that such areas also may have AQRVs to be taken into
consideration.
3. Protect Public Health and Welfare From Adverse Effects
Notwithstanding Attainment of NAAQS
The first goal and purpose in section 160 of the Act sets forth a
broad mission ``to protect public health and welfare from any actual or
potential adverse effects which in the Administrator's judgment may
reasonably be anticipated to occur notwithstanding attainment and
maintenance of all national ambient air quality standards.'' The
precise meaning of this goal is somewhat ambiguous because it appears
to mirror the legal standards applicable to the promulgation of the
primary and secondary NAAQS. Under section 109(b) of the Act, the
primary NAAQS must ``protect the public health'' with an adequate
margin of safety (section 109(b)(1)) and the secondary NAAQS must
``protect the public welfare from any known or anticipated adverse
effects'' associated with ambient concentrations of the pollutant
(section 109(b)(2)). The term ``welfare'' is defined in the Act to
include ``effects on soils, water, crops, vegetation, man-made
materials, animals, wildlife, weather, visibility, and climate.''
Section 302(h).
When applied as a relevant factor for the content of PSD
regulations for specific pollutants under section 166(c) of the Act, we
do not construe this language in section 160 to require EPA to conduct
a full NAAQS review every time it establishes PSD regulations for a
pollutant. A NAAQS review is a rigorous scientific process,\5\ and
Congress gave EPA 5 years to complete this review. 42 U.S.C.
7409(d)(1). However, under section 166(a) of the Act, Congress gave EPA
only 2 years to establish PSD regulations for specific pollutants.
Furthermore, in cases where NAAQS were not established as of 1977,
section 166(a) gave EPA 2 years after the establishment of a NAAQS to
promulgate PSD regulations. This indicates that Congress intended for
PSD regulations to be developed shortly after establishment of a NAAQS
and before completion of the next NAAQS review in 5 years. As a result,
we do not believe it is reasonable to interpret this factor to require
such a rigorous review to establish PSD regulations. In addition, as
discussed further below, we believe these statutory provisions indicate
that Congress intended for EPA to develop PSD rules using the research
compiled when establishing or reviewing a NAAQS.
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\5\ The NAAQS process begins with the development of ``air
quality criteria'' under section 108 for air pollutants that ``may
reasonably be anticipated to endanger public health or welfare'' and
that come from ``numerous or diverse'' sources. Section 108(a)(1).
``Air quality criteria'' must reflect the latest scientific
knowledge on ``all identifiable effects on public health or
welfare'' that may result from a pollutant's presence in the ambient
air. Id. Sec. 7408(a)(2). The scientific assessments constituting
air quality criteria generally take the form of a ``criteria
document,'' a rigorous review of all pertinent scientific studies
and related information. The EPA also develops a ``staff paper'' to
``bridge the gap'' between the scientific review and the judgments
the Administrator must make to set standards. See Natural Resources
Defense Council v. EPA (``NRDC''), 902 F.2d 962, 967 (DC Cir. 1990).
Both documents undergo extensive scientific peer-review as well as
public notice and comment. See e.g., 62 FR 38654/1-2.
For each NAAQS review, the Administrator must appoint ``an
independent scientific review committee composed of seven members of
the National Academy of Sciences, one physician, and one person
representing State air pollution control agencies,'' known as the
Clean Air Scientific Advisory Committee (CASAC). Section
109(d)(2)(A). CASAC is charged with recommending revisions to the
criteria document and NAAQS, and advising the Administrator on
several issues, including areas in which additional knowledge is
required to apprise the adequacy and basis of existing, new or
revised NAAQS. Section 109(d)(2)(B), (C).
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In the specific context of the PSD program, we construe this charge
to ``protect public health and welfare'' to require EPA to evaluate
whether adverse effects may occur as a result of increases in pollution
to ambient levels below the NAAQS. If such effects may occur in some
areas of the country, then EPA must consider how to establish PSD
regulations that protect public health and welfare against such effects
where they may occur. However, we do not interpret the PSD program to
require regulations that eliminate all adverse effects that may result
from increases in pollution in attainment areas. The PSD program is, as
its title suggests, designed to prevent ``significant deterioration''
from a baseline concentration. S. Rep. 95-127 at (3 LH at 1385) (``This
legislation defines `significant deterioration' in all clean air areas
as a specified amount of additional pollution. This definition is
intended to prevent any major decline in air quality currently existing
in clean air areas * * *''). That is, some decline in air quality
(relative to the baseline air quality concentration) is permissible for
any particular area of the country that is currently achieving the
NAAQS, as long as it is not ``significant.'' \6\
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\6\ Of course, if the area is designated nonattainment pursuant
to section 107 of the Act because the air quality is not attaining
the NAAQS, the PSD increments do not apply. Rather, reductions in
emissions must be implemented to bring the area's air quality into
attainment with the NAAQS, and, in the case of new sources,
sufficient offsetting emissions reductions must be obtained.
Sections 172(c) and 173(a) of the Act.
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[[Page 8888]]
4. Ensure Economic Growth Consistent With Preservation of Existing
Clean Air Resources
The third goal and purpose set forth in section 160 is to ``insure
that economic growth will occur in a manner consistent with the
preservation of existing clean air resources.'' To some extent, this
goal of the PSD program more specifically articulates the broader
purpose of the CAA, described in section 101(b)(1) of the Act, to
``protect and enhance the quality of the Nation's air resources so as
to promote the public health and welfare and the productive capacity of
its population.'' 42 U.S.C. 7401(b)(1). Sections 160(3) and 101(b)(1)
are similar in that both sections reflect the goal to simultaneously
protect air quality and to foster economic growth. Thus, in
interpreting the meaning of section 160(3) when used as a factor
applicable under section 166(c), we also consider the broader purpose
of the Act set forth in section 101(b)(1).
The first part of this goal of the PSD program set forth in section
160(3) (``to insure that economic growth will occur'') makes clear that
the PSD program is not intended to stifle economic growth. However, the
second part of this goal indicates that economic growth should ``occur
in a manner that is consistent with the preservation of existing clean
air resources.'' 42 U.S.C. 7470(3). Section 101(b)(1) indicates that
these goals are not necessarily inconsistent because Congress sought to
``protect and enhance the Nation's air resources so as to promote the
public health and welfare and the productive capacity of [the Nation's]
population.'' Thus, when considered in light of the purpose of the Act