Proposed Rule2026-00782

Determination of Attainment by the Attainment Date; 1997 Ozone Standards; California; Coachella Valley

Primary source

Metadata and text below are from the Federal Register, a public-domain U.S. government work. Always verify the official published version before relying on it for any legal matter.

Published
January 15, 2026

Issuing agencies

Environmental Protection Agency

Abstract

The Environmental Protection Agency (EPA) is proposing to determine that the Riverside County (Coachella Valley) 1997 ozone Extreme nonattainment area ("Coachella Valley") attained the 1997 ozone national ambient air quality standards (NAAQS) by its June 15, 2025, attainment date. This proposed determination is based on quality- assured and certified ambient air quality monitoring data from 2022 through 2024. We are taking comments on this proposal and plan to follow with a final action.

Full Text

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<title>Federal Register, Volume 91 Issue 10 (Thursday, January 15, 2026)</title>
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[Federal Register Volume 91, Number 10 (Thursday, January 15, 2026)]
[Proposed Rules]
[Pages 1732-1737]
From the Federal Register Online via the Government Publishing Office [<a href="http://www.gpo.gov">www.gpo.gov</a>]
[FR Doc No: 2026-00782]


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ENVIRONMENTAL PROTECTION AGENCY

40 CFR Part 52

[EPA-R09-OAR-2025-3127; FRL-13098-01-R9]


Determination of Attainment by the Attainment Date; 1997 Ozone 
Standards; California; Coachella Valley

AGENCY: Environmental Protection Agency (EPA).

ACTION: Proposed determination.

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SUMMARY: The Environmental Protection Agency (EPA) is proposing to 
determine that the Riverside County (Coachella Valley) 1997 ozone 
Extreme nonattainment area (``Coachella Valley'') attained the 1997 
ozone national ambient air quality standards (NAAQS) by its June 15, 
2025, attainment date. This proposed determination is based on quality-
assured and certified ambient air quality monitoring data from 2022 
through 2024. We are taking comments on this proposal and plan to 
follow with a final action.

DATES: Comments must be received on or before February 17, 2026.

ADDRESSES: Submit your comments, identified by Docket ID No. EPA-R09-
OAR-2025-3127 at <a href="https://www.regulations.gov">https://www.regulations.gov</a>. For comments submitted at 
<a href="http://Regulations.gov">Regulations.gov</a>, follow the online instructions for submitting 
comments. Once submitted, comments cannot be edited or removed from 
<a href="http://Regulations.gov">Regulations.gov</a>. The EPA may publish any comment received to its public 
docket. Do not submit electronically any

[[Page 1733]]

information you consider to be Confidential Business Information (CBI) 
or other information whose disclosure is restricted by statute. 
Multimedia submissions (audio, video, etc.) must be accompanied by a 
written comment. The written comment is considered the official comment 
and should include discussion of all points you wish to make. The EPA 
will generally not consider comments or comment contents located 
outside of the primary submission (i.e., on the web, cloud, or other 
file sharing system). For additional submission methods, please contact 
the person identified in the FOR FURTHER INFORMATION CONTACT section. 
For the full EPA public comment policy, information about CBI or 
multimedia submissions, and general guidance on making effective 
comments, please visit <a href="https://www.epa.gov/dockets/commenting-epa-dockets">https://www.epa.gov/dockets/commenting-epa-dockets</a>. If you need assistance in a language other than English or if 
you are a person with a disability who needs a reasonable accommodation 
at no cost to you, please contact the person identified in the FOR 
FURTHER INFORMATION CONTACT section.

FOR FURTHER INFORMATION CONTACT: Tom Kelly, EPA Region IX, 75 Hawthorne 
St., San Francisco, CA 94105; phone: (415) 972-3856; email: 
<a href="/cdn-cgi/l/email-protection#1c777970706532687473717d6f6c5c796c7d327b736a"><span class="__cf_email__" data-cfemail="82e9e7eeeefbacf6eaedefe3f1f2c2e7f2e3ace5edf4">[email&#160;protected]</span></a>.

SUPPLEMENTARY INFORMATION: Throughout this document, ``we,'' ``us,'' 
and ``our'' refer to the EPA.

Table of Contents

I. Background
    A. Regulatory Context
    B. Coachella Valley 1997 Ozone Designation, Classifications and 
SIP Revisions
II. EPA Analysis
    A. Applicable Statutory and Regulatory Provisions
    B. Determination of Attainment
    C. Monitoring Network Considerations
    D. Data Considerations
    E. Effects of This Proposed Determination
III. Action Summary
IV. Statutory and Executive Order Reviews

I. Background

A. Regulatory Context

    The Clean Air Act (CAA or ``Act'') requires the EPA to establish 
primary and secondary NAAQS for certain pervasive pollutants that ``may 
reasonably be anticipated to endanger public health and welfare.'' \1\ 
The primary NAAQS is designed to protect public health with an adequate 
margin of safety, and the secondary NAAQS is designed to protect public 
welfare and the environment. The EPA has set standards for six common 
air pollutants, referred to as criteria pollutants, including ozone. 
These standards represent the air quality levels an area must meet to 
comply with the CAA.
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    \1\ CAA section 108(a).
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    Ground-level ozone pollution is formed from the reaction of 
volatile organic compounds (VOC) and oxides of nitrogen 
(NO<INF>X</INF>) in the presence of sunlight.\2\ These two pollutants, 
referred to as ozone precursors, are emitted by many types of sources, 
including on- and off-road motor vehicles and engines, power plants and 
industrial facilities, and smaller area sources such as lawn and garden 
equipment and paints.
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    \2\ The State of California refers to reactive organic gases 
(ROG) rather than VOC in some of its ozone related SIP submissions. 
As a practical matter, ROG and VOC refer to the same set of chemical 
constituents, and for the sake of simplicity, we refer to this set 
of gases as VOC in this determination notification.
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    Scientific evidence indicates that adverse public health effects 
occur following exposure to ozone, particularly in children and adults 
with lung disease. Breathing air containing ozone can reduce lung 
function and inflame airways, which can increase respiratory symptoms 
and aggravate asthma or other lung diseases.\3\
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    \3\ EPA, Health Effects of Ozone Pollution, available at <a href="https://www.epa.gov/ground-levelozone-pollution/health-effects-ozone-pollution">https://www.epa.gov/ground-levelozone-pollution/health-effects-ozone-pollution</a>.
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    On July 18, 1997, the EPA revised the primary and secondary NAAQS 
for ozone to set the acceptable level of ozone in the ambient air at 
0.08 parts per million (ppm), averaged over an 8-hour period.\4\
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    \4\ 62 FR 38856 (July 18, 1997). Primary standards provide 
public health protection, including protecting the health of 
``sensitive'' populations such as asthmatics, children, and the 
elderly. Secondary standards provide public welfare protection, 
including protection against decreased visibility and damage to 
animals, crops, vegetation, and buildings. Since the primary and 
secondary standards established in 1997 are set at the same level, 
we refer to them herein using the singular ``1997 ozone NAAQS'' or 
``1997 ozone standards.''
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    The EPA set the 1997 ozone NAAQS over an 8-hour period based on 
scientific evidence demonstrating that ozone causes adverse health 
effects at lower concentrations and over longer periods of time than 
was understood when the pre-existing 1-hour ozone standards were set. 
The EPA determined that the 8-hour standards would be more protective 
of human health, especially for children and for adults who are active 
outdoors, and for individuals with a preexisting respiratory disease, 
such as asthma.
    In March 2008, the EPA completed another review of the primary and 
secondary ozone standards and tightened them further by lowering the 
level for both to 0.075 ppm.\5\ The EPA revoked the 1997 ozone NAAQS 
effective April 6, 2015; \6\ however, to comply with anti-backsliding 
requirements of the Act, areas designated nonattainment at the time 
that the 1997 ozone NAAQS was revoked remain subject to certain 
requirements based on their classification at the time of revocation.
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    \5\ 73 FR 16436 (March 27, 2008). The EPA further strengthened 
the primary and secondary eight-hour ozone NAAQS in October 2015 
from 0.075 ppm to 0.070 ppm. 80 FR 65291 (October 26, 2015). This 
action relates only to the 1997 ozone NAAQS.
    \6\ 80 FR 12264 (March 6, 2015).
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    The EPA's determination that an area failed to attain by its 
attainment date, which is made under CAA section 301 and consistent 
with section 181(b)(2), triggers these anti-backsliding requirements. 
See South Coast Air Quality Mgmt. Dist. v. EPA, 882 F.3d 1138, 1147 
(D.C. Cir. 2018). On October 26, 2015, the EPA again revised the level 
of the primary (and secondary) ozone NAAQS once more to 0.70 ppm.

B. Coachella Valley 1997 Ozone Designation, Classifications and SIP 
Revisions

    Following promulgation of a new or revised NAAQS, the EPA is 
required by the CAA to designate areas throughout the nation as 
attaining or not attaining the standards. Effective June 15, 2004, we 
designated nonattainment areas for the 1997 ozone standards.\7\ The 
designations and classifications for the 1997 ozone standards for 
California areas are codified at 40 CFR 81.305. In a rule governing 
certain facets of implementation of the 1997 ozone standards (the Phase 
1 Rule), the EPA classified the Coachella Valley as ``Serious'' for the 
1997 ozone standards, with an attainment date no later than June 15, 
2013.\8\ This classification applied to areas under the jurisdiction of 
the State of California and the areas of Indian country within the 
Coachella Valley.
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    \7\ 69 FR 23858 (April 30, 2004).
    \8\ 69 FR 23858 (April 30, 2004).
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    The Coachella Valley includes a part of the Colorado Desert in 
Riverside County, California, as well as parts of the adjacent mountain 
ranges. For a precise description of the geographic boundaries of the 
area, see 40 CFR 81.305. The Coachella Valley is under the jurisdiction 
of the South Coast Air Quality Management District (SCAQMD or 
``District''). The District and California Air Resources Board (CARB or 
``State'') are responsible for adopting and submitting a state 
implementation plan (SIP) to attain the 1997 ozone standards for 
nonattainment areas in

[[Page 1734]]

their jurisdiction. The District primarily regulates stationary sources 
while CARB regulates mobile sources.
    On November 28, 2007, CARB requested that the EPA reclassify the 
Coachella Valley 1997 ozone nonattainment area from ``Serious'' to 
``Severe-15.'' EPA's proposed rulemaking explained that California's 
request applied only to areas subject to the jurisdiction of the State 
of California.\9\ It further explained that the Tribes of the Coachella 
Valley had not requested authority to administer any Clean Air Act 
programs in Indian country. In such circumstances, the EPA implements 
relevant reclassification provisions of the CAA, and that EPA was 
proposing reclassification for the areas of Indian Country, following 
notification of Tribal leaders and an invitation for consultation.\10\ 
The EPA granted the reclassification request from CARB and finalized 
the reclassification of areas of Indian country to Severe, effective 
June 4, 2010, with an attainment date of not later than June 15, 
2019.\11\
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    \9\ 74 FR 43654 (August 27, 2009).
    \10\ Indian Country within the boundaries of the 1997 ozone 
nonattainment area are the Tribal lands of Agua Caliente Band of 
Cahuilla Indians of the Augustine Caliente Reservation, the 
Augustine Band of Cahuilla Indians, the Cabazon Band of Mission 
Indians, the Santa Rosa Band of Cahuilla Indians and the Torress 
Martinez Desert Cahuilla Indians and the Twenty-Nine Palms Band of 
Mission Indians of California.
    \11\ 75 FR 24409 (May 5, 2010).
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    On June 12, 2017, the EPA approved District and CARB submittals 
addressing many of the Severe nonattainment area planning requirements 
under the CAA for Coachella Valley.\12\ On June 11, 2019, the State 
requested a reclassification of Coachella Valley from ``Severe-15'' to 
``Extreme,'' which the EPA granted with an attainment date of not later 
than June 15, 2024.\13\ In a final rule dated September 5, 2025, EPA 
granted a one-year extension of the applicable attainment date to June 
15, 2025 at the State's request, upon finding the area satisfied the 
statutory criteria under CAA section 181(a)(5).\14\
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    \12\ 82 FR 26854 (June 12, 2017).
    \13\ 84 FR 32841 (July 10, 2019).
    \14\ 90 FR 42844 (September 5, 2025).
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    As explained in the action reclassifying the area to Extreme 
nonattainment, the EPA's reclassification only applied to the portions 
of the Coachella Valley subject to the State's jurisdiction, and the 
EPA did not reclassify any areas of Indian country within the 
boundaries of the nonattainment area. The EPA only reclassifies 
nonattainment areas to Extreme nonattainment on a voluntary basis. The 
timing of the State's request so close to the Severe nonattainment date 
did not allow the EPA sufficient time to consult with the Tribes of the 
Coachella Valley on their interest in a reclassification to Extreme 
nonattainment; however, the Tribes were notified of the planned action 
for part of the Coachella Valley subject to State jurisdiction.\15\
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    \15\ 84 FR 32841, 32842 (July 10, 2019).
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    On April 16, 2024, the EPA proposed approval of District and CARB 
submittals addressing many of the Extreme area planning requirements 
under the CAA for Coachella Valley.\16\ On June 12, 2024, the EPA 
finalized approval of certain elements of the Extreme area plan, 
including the attainment demonstration, but deferred action on the 
reasonable further progress demonstration and the vehicle miles 
traveled offset demonstration.\17\ On January 21, 2025, EPA finalized 
approval of the remaining elements of the plan, the vehicle miles 
traveled offset demonstration and the reasonable further progress 
demonstration.\18\ The State submitted a CAA 185 fee rule on August 13, 
2024, but the EPA has yet to act on that submittal.\19\
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    \16\ The proposal, 89 FR 26817 (April 16,2024), did not address 
the submittal's reasonably available control technology 
demonstration.
    \17\ 89 FR 49815 (June 12, 2024).
    \18\ 90 FR 6823 (January 21,2025).
    \19\ Letter from Steven S. Cliff CARB to Martha Guzman, EPA 
Region IX, dated August 9, 2024 and electronically submitted on 
August 13, 2024.
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    The State submitted a contingency measure for the 1997 ozone NAAQS 
as part of the Severe Area attainment Plan,\20\ but the State later 
withdrew the measure because it relied on previously implemented 
reductions.\21\ The nonattainment area's Extreme Area attainment plan 
explained the District's intent to amend SCAQMD Rule 445, ``Wood 
Burning Devices,'' to include potential contingency provisions for 
Coachella Valley for the 1997 ozone standards.\22\ To date, the EPA has 
not received a submittal to address the 1997 ozone contingency measures 
requirements of CAA sections 172(c)(9) and 182(c)(9) for the Coachella 
Valley.
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    \20\ Letter from James N. Goldstene, CARB, to Wayne Nastri, EPA 
Region IX, dated 11/28/2007.
    \21\ Letter from Richard Corey, CARB, to John Busterud, EPA 
Region IX, dated April 28, 2020. In Bahr v. EPA, 836 F.3d 1218, 
1235-1237 (9th Cir. 2016), the Ninth Circuit Court of Appeals held 
that already-implemented pollution control measures cannot be used 
as contingency measures. Instead, contingency measures must be 
conditional and prospective, meaning the measures are triggered by 
specific events and implemented to achieve emission reductions only 
after those events occur.
    \22\ ``Final Coachella Valley Extreme Area Plan for the 1997 8-
Hour Ozone Standard,'' South Coast Air Quality Management District, 
dated December 2020, and submitted to EPA in a letter from CARB 
dated December 29, 2020, p. 6-30.
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II. EPA Analysis

A. Applicable Statutory and Regulatory Provisions

    For the revoked 1997 ozone NAAQS, the EPA is required to determine 
whether an ozone nonattainment area attained the ozone standard by the 
area's attainment date solely for purposes of triggering any applicable 
anti-backsliding requirements. For Extreme areas, applicable 
requirements triggered upon a finding that an area failed to attain by 
the attainment date are nonattainment contingency measures and CAA 
section 185 fee programs.\23\ A determination of whether an area's air 
quality meets the 1997 ozone NAAQS is generally based on three years of 
complete, quality-assured, and certified air quality monitoring data 
gathered at established State and Local Air Monitoring Stations 
(``SLAMS'') in the area and entered into the EPA's Air Quality System 
(AQS) database.\24\ Data from ambient air monitors operated by state/
local agencies in compliance with EPA monitoring requirements must be 
submitted to the AQS database. Monitoring agencies annually certify 
that these data are accurate to the best of their knowledge. 
Accordingly, the EPA relies primarily on data in its AQS database when 
determining the attainment status of an area.\25\ All data are reviewed 
to determine the area's air quality status in accordance with 40 CFR 
part 50, appendix I.
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    \23\ 40 CFR 51.1105(d)(2)(iii).
    \24\ Generally, a ``complete'' data set for determining 
attainment of ozone NAAQS is one that includes three years of data. 
There are less stringent data requirements for showing that a 
monitor has failed an attainment test and thus has recorded a 
violation of the standard.
    \25\ 40 CFR 50.15; 40 CFR part 50, appendix I; 40 CFR part 53; 
40 CFR part 58, appendices A, C, D, and E.
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    Under EPA regulations at 40 CFR 50.10, an area attains the 1997 
ozone NAAQS when the 3-year average of the annual fourth-highest daily 
maximum 8-hour average ozone monitor concentrations is less than or 
equal to 0.08 ppm (i.e., 0.084 ppm when rounding, based on the 
truncating conventions in 40 CFR part 50, appendix I). This 3-year 
average is referred to as the ``design value.'' When the design value 
is greater than 0.084 ppm at any monitor within the area, then the area 
is violating the NAAQS.\26\

[[Page 1735]]

The data completeness requirement is met when the average percent of 
days with valid ambient monitoring data is greater than or equal to 90 
percent and no single year has less than 75 percent data completeness, 
as determined under appendix I of 40 CFR part 50.\27\
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    \26\ The data handling convention in 40 CFR part 50, appendix I 
dictates that concentrations shall be reported in ppm to the third 
decimal place, with additional digits to the right being truncated. 
Thus, a computed 3-year average ozone concentration of 0.085 ppm is 
greater than 0.08 ppm and would exceed the standard, but a design 
value of 0.084 is truncated to 0.08 and attains the 1997 ozone 
NAAQS.
    \27\ 40 CFR part 50, appendix I, section 2.3(b).
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B. Determination of Attainment

    Section 179(c) of the CAA requires that within six months following 
the applicable attainment date, the EPA shall determine whether an 
ozone nonattainment area attained the standard based on the area's 
design value as of that date.\28\ This determination, also referred to 
as a determination of attainment by the attainment date, is based on 
certified data leading up to the attainment date, i.e., in this case, 
data for 2022-2024. Section 179(c)(2) of the CAA requires the EPA to 
publish the determination in the Federal Register.
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    \28\ A determination that an area has attained by the applicable 
attainment date does not constitute a redesignation to attainment.
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    The EPA is proposing to determine that the Coachella Valley has 
attained the 1997 ozone NAAQS by its applicable attainment date; that 
is, that the average of the annual fourth-highest daily maximum 8-hour 
average ozone concentrations was at or below 0.084 ppm in the three 
years leading up to the applicable attainment date. This proposed 
determination is based on three years of quality-assured and certified 
ambient air quality monitoring data in AQS for the 2022-2024 monitoring 
period.
    The EPA's proposed determination of attainment is based upon data 
that have been collected and quality assured in accordance with 40 CFR 
part 58 and recorded in the EPA's AQS database.\29\ As discussed in 
section II.D of this document, ambient air quality monitoring data for 
the 3-year period preceding the attainment date (i.e., 2022-2024 for 
the 1997 ozone NAAQS for the Coachella Valley, based on the applicable 
attainment date of June 15, 2025) meet the data completeness 
requirements in 40 CFR part 50, appendix I.
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    \29\ The EPA maintains the AQS, a database that contains ambient 
air pollution data collected by the EPA, state, local, and Tribal 
air pollution control agencies. The AQS also contains meteorological 
data, descriptive information about each monitoring station 
(including its geographic location and its operator) and data 
quality assurance/quality control information. The AQS data is used 
to (1) assess air quality, (2) assist in attainment/non-attainment 
designations, (3) evaluate SIPs for nonattainment areas, (4) perform 
modeling for permit review analysis, and (5) prepare reports for 
Congress as mandated by the CAA. Access is through the website at 
<a href="https://www.epa.gov/aqs">https://www.epa.gov/aqs</a>.
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C. Monitoring Network Considerations

    Section 110(a)(2)(B)(i) of the CAA requires states to establish and 
operate air monitoring networks to compile data on ambient air quality 
for all criteria pollutants. The ambient air monitoring network in the 
Coachella Valley includes air monitoring stations that are managed and 
operated by SCAQMD. SCAQMD submits annual network plans to the EPA. 
These plans document the status of the District's air monitoring 
networks, as required under 40 CFR 58.10. The EPA reviews these annual 
network plans for compliance with specific requirements in 40 CFR part 
58. With respect to ozone, we have found that the annual network plans 
submitted by SCAQMD meet the minimum monitoring requirements of 40 CFR 
part 58.\30\
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    \30\ We have included copies of CARB and SCAQMD's annual network 
plans for 2022-2024 in the docket for this action, along with our 
reviews of these plans and our associated transmittal 
correspondence.
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    Finally, the EPA conducts regular Technical Systems Audits (TSAs) 
to review and inspect state and local ambient air monitoring programs 
to assess compliance with applicable regulations concerning the 
collection, analysis, validation, and reporting of ambient air quality 
data. As a Primary Quality Assurance Organization (PQAO) in California, 
SCAQMD is responsible for overseeing the quality of the data it 
collects. For the purposes of this determination, we reviewed the 
findings from the EPA's most recent TSA of the SCAQMD ambient air 
monitoring program.\31\ The results of this TSA found that the 
District's PQAO quality system was functioning well and produced ozone 
data suitable for use in regulatory decision-making. Therefore, the 
results of the TSA do not preclude the EPA from determining that the 
Coachella Valley has attained the 1997 ozone NAAQS.
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    \31\ Letter from Matthew Lakin, EPA to Dr. Jason Low, SCAQMD 
(Technical Systems Audit), dated June 6, 2025.
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D. Data Considerations

    In accordance with 40 CFR 58.15, SCAQMD annually certifies that the 
previous year's ambient concentration and quality assurance data are 
completely submitted to AQS and that the ambient concentration data are 
accurate, taking into consideration the quality assurance findings.\32\ 
The monitoring sites within the Coachella Valley for calendar years 
2022 through 2024 are located in Joshua Tree National Park, Palm 
Springs, and Indio. Table 1 of this document summarizes the ozone 
monitoring data from the monitoring sites by showing, if available, the 
annual 4th highest daily maximum concentrations and design values over 
the 2022-2024 period. The monitoring data is representative of the 
areas of Indian country as well as land under the jurisdiction of the 
State of California.
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    \32\ We have included SCAQMD's and CARB's annual data 
certifications for 2022, 2023, and 2024 in the docket for this 
action.

 Table 1--Coachella Valley Monitors With Valid Fourth High 8-Hour Ozone Average Concentrations and Design Values
                                               (ppm) for 2022-2024
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                                                                                 4th Highest daily maximum
          AQS site ID                   Site name           Design value  --------------------------------------
                                                            (2022-2024)        2022         2023         2024
----------------------------------------------------------------------------------------------------------------
060650010.....................  Joshua Tree National                0.070        0.070        0.071        0.070
                                 Park, Cottonwood
                                 Visitor Center.
060652007.....................  Indio-Amistad High            Invalid \b\      \a\ N/A      \a\ N/A        0.079
                                 School \a\.
060655001.....................  Palm Springs-Fire                   0.084        0.084    \c\ 0.083        0.087
                                 Station.
----------------------------------------------------------------------------------------------------------------
\a\ The former Indio-Jackson station closed April 20, 2022 and SCAQMD relocated the monitoring site to the
  nearby Indio-Amistad High School and began monitoring January 1, 2024. EPA approved this relocation on October
  29, 2024 after being notified via letter on April 2, 2024, and data from the old and new sites was combined to
  form one continuous data record for design value calculations.
\b\ The 2024 design value at the Indio--Amistad High School is invalid due to incomplete data capture in
  calendar years 2022 (30%) and 2023 (0%).
\c\ The 2023 design value excludes concurred upon wildfire-driven exceedances of the 1997 ozone NAAQS at the
  Palms Springs--Fire Station monitoring site on July 14-15, 2023, under the Exceptional Events Rule.
Source: EPA, AQS Design Value (AMP480), Report Request ID: May 27, 2025.


[[Page 1736]]

    Consistent with the requirements contained in 40 CFR part 50, the 
EPA has reviewed the quality-assured and certified ozone ambient air 
monitoring data for completeness. The EPA reviewed the data as recorded 
in AQS for the applicable monitoring period, collected at the 
monitoring sites in the Coachella Valley, and has determined that the 
data are generally complete, with the exception of the Indio-Amistad 
High School monitor. The former Indio-Jackson monitoring site was 
closed April 20, 2022, due to loss of the lease and reopened at the 
nearby Indio-Amistad High School location on January 1, 2024. SCAQMD 
notified the EPA of this closure via letter on April 2, 2024, and 
documented it in its 2024 annual network plan. The combined data for 
the Indio-Jackson Street and Indio-Amistad monitoring sites had design 
values that were 0.003-0.013 ppm lower than the highest design value 
site for the previous ten valid design value years (2011-2022) \33\ and 
has had design values below the 1997 ozone NAAQS since 2020. In 
addition, the 2024 4th highest daily maximum concentration observed at 
the Indio-Amistad High School monitoring site was below the level of 
the 1997 ozone NAAQS and 0.008 ppm lower than that observed at Palm 
Springs-Fire Station.
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    \33\ AQS Design Value (AMP480), Report Request ID: 2294814, May 
27, 2025.
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    The remaining ozone monitoring sites meet the data completeness 
requirements of 40 CFR part 50, Appendix I, and, therefore, the data 
summarized in table 1 of this document are considered complete for the 
purposes of determining if the standard is met. In light of the extent 
and reliability of the applicable ozone monitoring network, and the 
data collected from that network and summarized in table 1 of this 
document, we are proposing to determine that the Coachella Valley 
attained the revoked 1997 ozone NAAQS (as defined in 40 CFR part 50, 
appendix I) by the applicable attainment date (i.e., June 15, 2025).

E. Effects of This Proposed Determination

    A determination of attainment by the attainment date does not have 
the effect of redesignating an area to attainment. Redesignation of an 
area to attainment requires that an area has met all applicable 
requirements of CAA section 110 and part D, and that the area has 
submitted, and the EPA has approved, a redesignation request and 
maintenance plan.\34\ Therefore, if we finalize this determination as 
proposed, Coachella Valley will remain designated nonattainment for the 
1997 ozone NAAQS and will retain its current classification of Extreme 
for this standard. In addition, a final determination of attainment by 
the extended Extreme area attainment date would not apply to Tribal 
land, because areas of Indian country in the Coachella Valley 
nonattainment area remained classified as Severe nonattainment 
following EPA's action on the voluntary reclassification request to 
Extreme of state land from CARB and the SCAQMD.\35\
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    \34\ Memorandum dated September 4, 1992 from John Calcagni, EPA, 
to Regional Air Directors, titled ``Procedures for Processing 
Requests to Redesignate Areas to Attainment.''
    \35\ 84 FR 32841 (July 10, 2019).
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    If we finalize our proposed determination that the Coachella Valley 
has attained the 1997 ozone NAAQS by the attainment date, then 
attainment contingency measures for the 1997 ozone NAAQS would never be 
required to be implemented, regardless of whether the area continued to 
attain the NAAQS, and Reasonable Further Progress contingency measures 
could not be triggered and would therefore no longer be necessary.\36\ 
In addition, the Coachella Valley would not collect CAA section 185 
fees. A final determination of attainment, however, would not prevent 
the EPA from exercising its authority under the CAA to address any 
subsequent violations of the NAAQS.
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    \36\ See, e.g., 87 FR 42126, 42130 (July 14, 2022). See also 57 
FR 13498, 13564 (April 16, 1992) and Memorandum dated May 10, 1995, 
from John D. Seitz, EPA, to EPA Regional Air Directors, Regions I-X, 
Subject: ``Reasonable Further Progress, Attainment Demonstration, 
and Related Requirements for Ozone Nonattainment Areas Meeting the 
Ozone National Ambient Air Quality Standard,'' p. 4.
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III. Action Summary

    We are proposing to determine that the Coachella Valley has 
attained the revoked 1997 ozone NAAQS by its June 15, 2025, attainment 
date, based on quality-assured and certified ambient air quality 
monitoring data from 2022 through 2024. The EPA is soliciting public 
comments on this proposed action, our rationale for the proposed 
action, and any other pertinent matters related to the proposed 
decision. We will accept comments from the public on this proposal for 
the next 30 days and will consider comments before taking final action.

IV. Statutory and Executive Order Reviews

    Under the CAA, the Administrator is required to approve a SIP 
submission that complies with the provisions of the Act and applicable 
Federal regulations 42 U.S.C. 7410(k); 40 CFR 52.02(a). Thus, in 
reviewing SIP submissions, the EPA's role is to approve State choices, 
provided that they meet the criteria of the CAA. Accordingly, this 
action merely approves State law as meeting Federal requirements and 
does not impose additional requirements beyond those imposed by State 
law. For that reason, this proposed action:
    <bullet> Is not a significant regulatory action subject to review 
by the Office of Management and Budget under Executive Order 12866 (58 
FR 51735, October 4, 1993);
    <bullet> Is not subject to Executive Order 14192 (90 FR 9065, 
February 6, 2025) because SIP actions are exempt from review under 
Executive Order 12866;
    <bullet> Does not impose an information collection burden under the 
provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et seq.);
    <bullet> Is certified as not having a significant economic impact 
on a substantial number of small entities under the Regulatory 
Flexibility Act (5 U.S.C. 601 et seq.);
    <bullet> Does not contain any unfunded mandate or significantly or 
uniquely affect small governments, as described in the Unfunded 
Mandates Reform Act of 1995 (Pub. L. 104-4);
    <bullet> Does not have federalism implications as specified in 
Executive Order 13132 (64 FR 43255, August 10, 1999);
    <bullet> Is not subject to Executive Order 13045 (62 FR 19885, 
April 23, 1997) because it approves a State program;
    <bullet> Is not a significant regulatory action subject to 
Executive Order 13211 (66 FR 28355, May 22, 2001); and
    <bullet> Is not subject to requirements of section 12(d) of the 
National Technology Transfer and Advancement Act of 1995 (15 U.S.C. 272 
note) because application of those requirements would be inconsistent 
with the CAA.
    In addition, the SIP is not approved to apply on any Tribal land or 
in any other area where the EPA or an Indian Tribe has demonstrated 
that a Tribe has jurisdiction. In those areas of Indian country, the 
rule does not have Tribal implications and will not impose substantial 
direct costs on Tribal governments or preempt Tribal law as specified 
by Executive Order 13175 (65 FR 67249, November 9, 2000).

[[Page 1737]]

List of Subjects in 40 CFR Part 52

    Environmental protection, Air pollution control, Incorporation by 
reference, Intergovernmental relations, Nitrogen oxides, Ozone, 
Reporting and recordkeeping requirements, Volatile organic compounds.

    Dated: January 5, 2026.
Michael Martucci,
Acting Regional Administrator, Region IX.
[FR Doc. 2026-00782 Filed 1-14-26; 8:45 am]
BILLING CODE 6560-50-P


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This is legal information, not legal advice. Laws vary by jurisdiction and change frequently. Always verify current law with official sources and consult a licensed attorney in your jurisdiction for advice on your specific situation.