# Phoenix Ozone Nonattainment Area, Clean Air Act Section 182(f) Exemption Petition

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URL: https://www.frixlaw.com/law-library/documents/fr%3A94-27018

## Record

- **Collection:** Federal Register
- **Document type:** Uncategorized Document
- **Published:** November 1, 1994

## Text

ENVIRONMENTAL PROTECTION AGENCY

40 CFR Part 52

[AZ34-1-6418; FRL-5100-3]

Phoenix Ozone Nonattainment Area, Clean Air Act Section 182(f)
Exemption Petition

AGENCY: Environmental Protection Agency (EPA).

ACTION: Notice of proposed rulemaking (NPRM).

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SUMMARY: The EPA is proposing to approve a petition submitted by the
Arizona Department of Environmental Quality (ADEQ) requesting that the
EPA grant an exemption for the Phoenix ozone nonattainment area
(Phoenix Area) from the requirement to implement oxides of nitrogen
(NOX) Reasonably Available Control Technology (RACT). In
accordance with the requirements of the Clean Air Act, as amended in
1990 (the Act or CAA), the Phoenix area may be exempted from the
NOX reduction requirements where the Administrator determines that
net air quality benefits are greater in the absence of NOX
reductions from the sources concerned or that additional NOX
reductions would not contribute to attainment of the national ambient
air quality standard (NAAQS) for ozone. The ADEQ petition uses the
Urban Airshed Model (UAM) to demonstrate that additional NOX
reductions in the Phoenix Area would not contribute to attainment of
the ozone NAAQS. The EPA is proposing to exempt the Phoenix Area from
the requirement to implement NOX RACT and the applicable NOX
general and transportation conformity requirements. The EPA is
proposing approval of this action under provisions of the CAA regarding
plan requirements for nonattainment areas.

DATES: Comments on this proposed action must be received in writing on
or before December 1, 1994.

ADDRESSES: Comments may be mailed to: Daniel A. Meer, Chief, Rulemaking
Section (A-5-3), Air and Toxics Division, U.S. Environmental Protection
Agency, Region IX, 75 Hawthorne Street, San Francisco, CA 94105.
Copies of the exemption petition are available for public
inspection at EPA's Region 9 office during normal business hours.
Copies of the submitted petition may be obtained from the following
locations:

Rulemaking Section (A-5-3), Air and Toxics Division, U.S. Environmental
Protection Agency, Region IX, 75 Hawthorne Street, San Francisco, CA
94105.
Arizona Department of Environmental Quality, 3033 North Central Avenue,
Phoenix Arizona 85012.
Maricopa County Air Pollution Control District, 2406 S. 24th Street,
suite E214, Phoenix, Arizona 85034.

FOR FURTHER INFORMATION CONTACT: Wendy Colombo, Rulemaking Section (A-
5-3), or Scott Bohning, Air Quality Section (A-2-4), Air and Toxics
Division, U.S. Environmental Protection Agency, Region IX, 75 Hawthorne
Street, San Francisco, CA 94105 Telephone: (415) 744-1202; (415) 744-
1293.

SUPPLEMENTARY INFORMATION:

Background

On November 15, 1990, the Clean Air Act Amendments of 1990 were
enacted. Public Law 101-549, 104 Stat. 2399, codified at 42 U.S.C.
7401-7671q. The air quality planning requirements for the reduction of
NOX emissions are set out in section 182(f) of the CAA. On
November 25, 1992, EPA published a NPRM (57 FR 55620) entitled, ``State
Implementation Plans; Nitrogen Oxides Supplement to the General
Preamble; Clean Air Act Amendments of 1990 Implementation of Title I;
Proposed Rule,'' (the NOX Supplement) which describes the
requirements of section 182(f). The November 25, 1992, notice should be
referred to for further information on the NOX requirements and is
incorporated into this document by reference.
Section 182(f) of the Act requires States to apply the same
requirements to major stationary sources of NOX (``major'' as
defined in section 302 and section 182(c), (d), and (e)) as are applied
to major stationary sources of volatile organic compounds (VOCs). These
requirements are RACT and New Source Review (NSR) for major stationary
sources in certain ozone nonattainment areas.
The RACT requirements for major stationary sources of VOCs are
contained in section 182(b)(2), while the NSR requirements are
contained in section 182(a)(2)(C) and other provisions of section 182.
Section 182(b)(2) requires submittal of RACT rules for major stationary
sources of VOC emissions (not covered by a pre-enactment control
technologies guidelines (CTG) document or a post-enactment CTG
document) by November 15, 1992. There were no NOX CTGs issued
before enactment, and EPA has not issued a CTG document for any
NOX sources since enactment of the CAA. Section 182(a)(2)(C)
requires submittal of NSR rules incorporating the new preconstruction
permitting requirements for new or modified sources. The RACT and NSR
rules were required to be submitted by November 15, 1992.
The Phoenix area is classified as a moderate1 nonattainment
area for ozone; therefore this area is subject to the RACT and NSR
requirements cited above and the November 15, 1992 deadline.2 On
April 13, 1994, the State of Arizona submitted a petition to the EPA
requesting that the Phoenix area be exempted from the requirement to
implement NOX RACT measures pursuant to section 182(f) of the CAA.
The exemption request is based on UAM modeling conducted in accordance
with EPA guidelines.
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\1\ The Maricopa County ozone nonattainment area was
redesignated nonattainment and was classified by operation of law
pursuant to sections 107(d) and 181(a) upon the date of enactment of
the CAA. See 55 FR 56694 (November 6, 1991).
\2\ The State of Arizona was issued a finding of nonsubmittal
for the section 182(f) NOX RACT requirements on April 21, 1993,
and subsequently submitted a commitment on April 23, 1993 to adopt
and submit the NOX RACT rules. The commitment was submitted as
an interim measure to satisfy the NOX RACT requirements, and
proposed that the Maricopa County Bureau of Air Pollution Control
(MCBAPC) would develop the NOX RACT rules for submittal in
January 1994. The rules were to be developed at the same time that
the Maricopa Association of Governments (MAG) was conducting UAM for
the 1994 attainment demonstration requirements. If the UAM modeling
showed that NOX reductions would not contribute to attainment
of the ozone standard, then Arizona would petition for a section
182(f) exemption from the NOX RACT requirements.
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General Criteria--Section 182(f) Exemption Requests

The NOX RACT petition was submitted in accordance with the EPA
guidance document entitled, Guideline for Determining the Applicability
of Nitrogen Oxides Requirements Under Section 182(f) issued on December
16, 1993 (exemption guidance). In addition to the exemption guidance,
EPA's NOX exemption policy is contained in two memoranda\3\
providing that under section 182(f)(1)(A), an exemption from the
NOX requirements may be granted for nonattainment areas outside
the ozone transport region (OTR) if EPA determines that additional
reductions of NOX would not contribute to attainment of the NAAQS
for those areas. EPA's approval of monitoring-based NOX exemptions
are granted on a contingent basis and last for only as long as the
area's monitoring data continue to demonstrate attainment. As described
below, EPA's approval of modeling-based NOX exemptions are also
granted on a contingent basis.
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\3\Michael H. Shapiro, Acting Assistant Administrator for Air
and Radiation, dated September 17, 1993, entitled ``State
Implementation Plan (SIP) Requirements for Areas Submitting Requests
for Redesignation to Attainment of the Ozone and Carbon Monoxide
(CO) National Ambient Air Quality Standards (NAAQS) on or after
November 15, 1992'', and a subsequent revision to this memorandum
from John S. Seitz, Director of EPA's Office of Air Quality Planning
and Standards, issued on May 27, 1994, entitled, ``Section 182(f)
Nitrogen Oxides (NOX) Exemptions--Revised Process and
Criteria''.
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EPA's conformity rules4, 5 also reference the section 182(f)
exemption process as a means for exempting affected areas from NOX
conformity requirements.6 Therefore, ozone nonattainment areas
that are granted areawide section 182(f) exemptions under this approach
will also be exempt from the NOX general and transportation
conformity requirements.
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\4\``Criteria and Procedures for Determining Conformity to State
or Federal Implementation Plans or Transportation Plans, Programs,
and Projects Funded or Approved under Title 23 U.S.C. of the Federal
Transit Act'', November 24, 1993 (58 FR 62188).
5``Determining Conformity of General Federal Actions to
State or Federal Implementation Plans; Final Rule'', November 30,
1993 (58 FR 63214).
\6\The section 182(f) exemption is explicitly referred to and is
described in similar language in 40 CFR 51.394(b)(3)(i), the
``Applicability'' section of the transportation conformity rule, and
in the preamble (see 58 FR 62197, November 24, 1993). The language
is repeated in the provisions of the rule regarding the motor
vehicle emissions budget test [section 51.428(a)(1)(ii)] and the
``build/no-build'' test [sections 51.436(e), 51.438(e)], although
section 182(f) of the Act is not specifically mentioned. In the
general conformity rule, the section 182(f) NOX exemption is
referred to in section 51.852 (definition of ``Precursors of a
criteria pollutant'') and is discussed in the preamble (see 58 FR
63240, November 30, 1993).
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The EPA first provided guidance on NOX exemptions in the
NOX Supplement. The guidance states that EPA would rescind a
NOX exemption in cases where NOX reductions were later found
to be beneficial to an area's ability to attain and maintain the ozone
NAAQS. That is, a modeling-based exemption would last for only as long
as the areas's modeling continues to demonstrate attainment without
NOX reductions from major stationary sources.
If EPA later determines that NOX reductions are beneficial
based on new photochemical grid modeling in an area initially exempted,
the area would be removed from exempt status and would be required to
implement the NOX requirements, except to the extent modeling
shows that the NOX reductions are excess reductions.7 A
determination that the NOX exemption no longer applies would mean
that the NOX general and transportation conformity provisions
would again be applicable (see 58 FR 63214; 58 FR 62188; 59 FR 31238)
to the affected area. The NOX requirements would also re-apply,
although some reasonable time period after the EPA determination may be
provided for sources to meet the RACT limits. EPA expects this time
period to be as expeditious as practicable, taking into account any
current and applicable State or Federal regulations.
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\7\Section 182(f)(2) states that the application of the new
NOX requirements may be limited to the extent necessary to
avoid excess reductions of NOX as determined by applying tests
similar to the net air quality benefits test, the contribute to
attainment test, and the net ozone air quality benefits test.
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The subsequent modeling analyses alluded to above need not be
limited to the purpose of demonstrating attainment in the 1994 SIP
revisions. For example, future modeling might also be initiated to
resolve issues related to transport of ozone and ozone precursors into
downwind nonattainment areas. State or local officials might want to
consider a strategy that phases in NOX reductions only after
certain VOC reductions are implemented. As improved emission
inventories and ambient data become available, planning officials may
choose to remodel. In addition, alternative control strategy scenarios
might be considered in subsequent modeling analyses in order to improve
the cost-effectiveness of the attainment plan.
EPA's exemption guidance provides that pursuant to the requirements
of section 110(a)(2), States should consider evidence, such as
photochemical grid modeling, which shows that granting the NOX
exemption would interfere with attainment or maintenance in downwind
areas. The State of Arizona has not yet implemented NOX RACT, and
at the time of this notice, EPA has not received evidence from the
Phoenix Area or any downwind areas that shows that granting the
NOX exemption for the Phoenix Area would interfere with attainment
or maintenance in downwind areas.

Exemption Modeling Requirements

The policy documents cited above which contain guidance on the
petition requirements state that the modeling performed for the
petition should follow the Guideline on Regulatory Application of the
Urban Airshed Model, EPA-450/91-013, July 1991, (UAM guideline). The
UAM guideline describes procedures for the appropriate use of UAM, such
as for attainment demonstrations required of all ozone nonattainment
areas.
Section 182(f) of the CAA recognizes that although VOC and NOX
emissions are both precursors to ozone, in certain circumstances the
reduction of NOX emissions can actually increase ozone
concentrations. This occurs because two competing groups of chemical
reactions are affected by NOX. NOX emissions reduction
reduces one of the basic materials needed for ozone production, but it
also enhances the formation of hydrocarbon radicals, thus increasing
another basic ozone ingredient. Which effect dominates, if any, depends
on the ratio of VOC to NOX in the atmosphere, temperature, and
other factors. The atmosphere is said to be ``NOX-limited'' if
NOX reductions decrease peak ozone concentrations, and ``VOC-
limited'' if NOX reductions increase peak ozone concentrations.
UAM can simulate ozone photochemistry to determine the effects of VOC
and NOX emission reductions on ozone. Therefore, if these
simulations demonstrate that NOX emission reductions are of no
benefit or are counter-productive, then an exemption under section
182(f) would apply.
The NOX exemption guidance sets forth two possible tests for
showing that NOX emission reductions are of no benefit or are
counter-productive to ozone attainment for areas outside the OTR. The
petition must show that one or both of these tests is/are passed.
(i) Net air quality benefit: Show that the required NOX
reductions from the potential exempted sources are counter-productive
for overall air quality, primarily considering the modeled effect on
the number of ozone NAAQS exceedances. Also considered are welfare,
visibility, toxic pollutants, the effect on secondary PM10
formation, etc. This must include UAM modeling reflecting an area's
submitted ozone attainment demonstration, with adopted control
measures.
(ii) Contribute to attainment: This test uses UAM modeling to show
that substantial reductions of VOC emissions result in lower ozone
levels than substantial reductions of NOX emissions AND combined
reductions of VOC and NOX emissions.8 The maximum one-hour
ozone concentrations from these three scenarios are then compared.
These three UAM simulations need not be tied to an actual attainment
demonstration9, but the modeled ``NOX reductions should be as
source-specific as possible, rather than across-the-board'' (p.27), and
should reflect ``baseline'' NOx reductions that are expected to occur
without the exemption.
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\8\``Substantial VOC reduction'' means that required to show
attainment, and ``substantial NOx reduction'' means a similar
percentage reduction.
\9\If an exemption is being requested for only certain NOX
sources, then the chosen test is to determine whether just the
``excess emission reductions'' from these sources would be counter-
productive; in this case, the test must be tied to an actual
submitted attainment demonstration.

The UAM guideline describes procedures for applying UAM, such as
choosing ozone episodes and the geographical domain to model, setting
emissions and meteorological inputs, setting boundary conditions to the
model, and evaluating the model's performance. The reliance of the
NOX exemption guidance on the UAM guideline is intended to ensure
that the model is used in a scientifically appropriate manner. Portions
of the UAM guideline that are specific to SIP attainment demonstrations
may not always be applicable to modeling used specifically for NOX
exemptions.

Description of Submitted Petition

The petition submitted by the ADEQ first briefly describes the
methodology used. Then, citing UAM modeling results of simulations
required for the chosen exemption test (the contribute to attainment
test), it concludes that the test is passed. In an appendix (Exhibits
1-4), the petition notes revisions to the emission inventory input made
after the cited Addenda to the MAG 1993 Ozone Plan for the Maricopa
County Area was prepared, and includes descriptions and graphs of UAM
modeling performance indicators and concentration results cited in the
main text.
The contribute to attainment test applied in the petition requires
a showing that substantial reductions of VOC yield a lower ozone peak
than do reductions of NOX, and of both VOC and NOX. In order
to make the modeling as source-specific as possible (required by the
exemption guidance), UAM simulations were also performed to examine the
effects of possible NOX RACT reductions at specific NOX
sources in the Maricopa County nonattainment area.
The ozone episodes chosen for modeling were the August 9-10, 1992
episode, which is the base case modeling described in Exhibit 2 (of the
petition) in an abbreviated form, and the June 13-14, 1993 episode. The
petition notes that there is only a single meteorological regime
associated with ozone NAAQS violations in Phoenix, due to stable
weather patterns, its ``island'' location which isolates the area from
other urban complexes, and its generally even distribution in size and
location of NOX emissions throughout the area. The reduction
levels chosen for the three 1996 modeled scenarios for each simulation
are as follows:

Episode 1

(1) A 20% VOC reduction, and a 0% NOX reduction;
(2) a 0% VOC reduction, and a 60% NOX reduction; and
(3) a 40% reduction of both VOC and NOX.
The results of these reduction simulations are described and
illustrated in Exhibit 1 of the petition. The ozone peaks are 11.9
parts per hundred million (pphm), 16.5 pphm, and 12.8 pphm,
respectively. Since the 11.9 pphm value, corresponding to the VOC-only
reduction, is the lowest, the test is passed. Also noted for this
scenario is the lowest area covered by high ozone concentrations.

Episode 2

(1) A 20% VOC reduction, and a 0% NOX reduction;
(2) a 0% VOC reduction, and a 20% NOX reduction; and
(3) a 20% reduction of both VOC and NOX.
The results of these reduction simulations are described and
illustrated in attachment 1 of the Technical Support Document (TSD).
The ozone peaks are 11.1 pphm, 14.6 pphm, and 13.0 pphm, respectively.
Since the 11.1 pphm value, corresponding to the VOC-only reduction, is
the lowest, this test is also passed.
The petition also describes modeling of 1996 emissions (including
adopted and committed control measures), with and without RACT applied
to specific NOX sources (this modeling is explained in attachment
1 of the TSD). Exhibit 1 of the petition states that the total NOX
reductions from potential NOX RACT measures for the August episode
is 50.6% of the large point source emissions, or 5.4% of the total
NOX emissions for the second day of the ozone episode (August 10).
These yielded a 0.1 pphm ozone increase. For the June episode, with a
52.5% reduction in elevated point source NOX emissions and a 6.9%
reduction in total NOX emissions, the results showed no impact on
the maximum simulated concentration. As referred to above, a more
detailed discussion of the petition can be found in the Technical
Support Document, dated October 1994.

Evaluation of Submitted Petition

The petition correctly utilizes an appropriate test from the
NOX exemption guidance. The ``contribute to attainment'' test is
available to nonattainment areas outside an OTR, and need not be tied
to an adopted and submitted attainment demonstration.
The single meteorological regime and the August 9-10, 1992 and June
13-14, 1993 ozone episodes used in the three required reduction
scenarios are described in the modeling protocol used for the Phoenix
Area's ozone attainment demonstration due November 15, 1994. For
attainment demonstrations, the UAM guideline requires an area with a
single regime to model three episodes of that meteorological type. The
intent in requiring that the UAM guideline be followed is to ensure
that the UAM is utilized in a scientifically appropriate manner and to
ensure that multiple meteorological regimes are addressed, if
necessary. However, in cases where an area is using intensive data from
a field study, a minimum of two episodes is acceptable. This is
appropriate where a field study is conducted that provides more
comprehensive data for the modeling analysis. The field study was
conducted during the summer of 1992 and provided more air quality and
meteorological data than is routinely available.
Since 1996 is the required attainment year for a moderate ozone
nonattainment area, the 1996 year is appropriate for use in the
analysis using UAM simulations.
The NOX and VOC reduction levels used in the test were
``substantial'' within the meaning of the exemption guidance, and
provide a reasonable basis for comparisons of their effect on ozone.
The additional simulations of NOX RACT reductions at specific
sources meet the exemption guidance requirement that the test be as
source-specific as possible, and further substantiate the conclusion
that implementation of NOX RACT for major stationary sources would
not contribute to attainment.

EPA Proposed Action

This action proposes to exempt the Phoenix ozone nonattainment area
from implementing the NOX RACT requirements and the general and
transportation conformity regulations for NOX. It is based on UAM
modeling for two episodes in the Phoenix area which demonstrate that
NOX reductions do not contribute to attainment. The final action
on this proposal will serve as a final determination that the finding
of nonsubmittal for the NOX RACT requirements has been corrected
and that on the effective date of the final action on this proposal,
any Federal Implementation Plan (FIP) clock is stopped.
Nothing in this action should be construed as permitting or
allowing or establishing a precedent for any future implementation
plan. Each request for a section 182(f) exemption shall be considered
separately in light of specific technical, economic, and environmental
factors and in relation to relevant statutory and regulatory
requirements.

Regulatory Process

The Office of Management and Budget has exempted this regulatory
action from Executive Order 12866 review.
Under the Regulatory Flexibility Act, 5 U.S.C. 600 et seq., EPA
must prepare a regulatory flexibility analysis assessing the impact of
any proposed or final rule on small entities. 5 U.S.C. 603 and 604.
Alternatively, EPA may certify that the rule will not have a
significant impact on a substantial number of small entities. Small
entities include small businesses, small not-for-profit enterprises and
government entities with jurisdiction over population of less than
50,000.
This exemption action does not create any new requirements, but
allows suspension of the indicated requirements for the life of the
exemption. Therefore, because the proposed approval does not impose any
new requirements, I certify that it does not have a significant impact
on any small entities affected. Moreover, due to the nature of the
Federal-state relationship under the CAA, preparation of a regulatory
flexibility analysis would constitute Federal inquiry into the economic
reasonableness of state action. The CAA forbids EPA to base its actions
concerning SIPs on such grounds. Union Electric Co. v. U.S. E.P.A., 427
U.S. 246, 256-66 (S. Ct. 1976); 42 U.S.C. 7410 (a)(2).
Under section 307(b)(1) of the CAA, petitions for judicial review
of this action must be filed in the United States Court of Appeals for
the appropriate circuit by December 1, 1994. Filing a petition for
reconsideration by the Administrator of this rule does not affect the
finality of this rule for the purposes of judicial review nor does it
extend the time within which a petition for judicial review may be
filed, and shall not postpone the effectiveness of such a rule.
This action may not be challenged later in proceedings to enforce
its requirements. Section 307(b)(2).

List of Subjects in 40 CFR Part 52

Environmental protection, Air pollution control, Hydrocarbons,
Intergovernmental relations, Nitrogen dioxide, Ozone, Reporting and
recordkeeping requirements, Volatile organic compounds.

Dated: October 25, 1994.
Carol M. Browner,
Administrator.

Part 52, chapter I, title 40 of the Code of Federal Regulations is
proposed to be amended as follows:

PART 52--[AMENDED]

1. The authority citation for part 52 continues to read as follows:

Authority: 42 U.S.C. 7401-7671q.

Subpart D--Arizona

2. Subpart D is proposed to be amended by adding Sec. 52.235 to
read as follows:

Sec. 52.235 Control strategy for ozone: Oxides of nitrogen.

EPA is approving an exemption request submitted by the State of
Arizona on April 13, 1994 for the Maricopa County ozone nonattainment
area from the NOX RACT requirements contained in section 182(f) of
the Clean Air Act. This approval exempts the area from implementing
reasonably available control technology (RACT) for major stationary
sources of nitrogen oxides (NOX) and the NOX related
requirements of general and transportation conformity regulations. The
exemption is based on Urban Airshed Modeling as would last for only as
long as the area's modeling continues to demonstrate attainment without
NOX reductions from major stationary sources.

[FR Doc. 94-27018 Filed 10-31-94; 8:45 am]
BILLING CODE 6560-50-P

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Source: Frix Law Library, https://www.frixlaw.com/law-library/documents/fr%3A94-27018. Public record. Not legal advice.
