Committee for a Better Arvin v. United States Environmental Protection Agency
CourtCourt of Appeals for the Ninth Circuit
Date FiledAugust 5, 2026
Docket24-7270
StatusPublished
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Full Opinion
FOR PUBLICATION
UNITED STATES COURT OF APPEALS
FOR THE NINTH CIRCUIT
No. 24-7270
COMMITTEE FOR A BETTER
ARVIN, a nonprofit corporation;
Agency No.
MEDICAL ADVOCATES FOR
EPA–R09–OAR–
HEALTHY AIR, a nonprofit
2023–0477
corporation; NATIONAL PARKS
CONSERVATION ASSOCIATION,
Environmental
a nonprofit corporation; SIERRA
Protection Agency
CLUB, a nonprofit corporation,
OPINION
Petitioners,
v.
UNITED STATES
ENVIRONMENTAL PROTECTION
AGENCY; MICHAEL REGAN, in
his official capacity as Administrator
of the U.S. Environmental Protection
Agency; MARTHA GUZMAN
ACEVES, Regional Administrator of
Region 9 of U.S., in her official
capacity as Regional Administrator
for Region IX of the U.S.
Environmental Protection Agency,
Respondents,
2 COMM. FOR A BETTER ARVIN V. U.S. EPA
----------------------------------------
CALIFORNIA AIR RESOURCES
BOARD; SAN JOAQUIN VALLEY
UNIFIED AIR POLLUTION
CONTROL DISTRICT,
Intervenors.
On Petition for Review of an Order of the
Environmental Protection Agency
Argued and Submitted November 19, 2025
San Francisco, California
Filed August 5, 2026
Before: Sidney R. Thomas, Daniel A. Bress, and Salvador
Mendoza, Jr., Circuit Judges.
Opinion by Judge Mendoza, Jr.;
Dissent by Judge Bress
COMM. FOR A BETTER ARVIN V. U.S. EPA 3
SUMMARY*
Clean Air Act
The panel remanded without vacatur in a case
challenging a final rule issued by the United States
Environmental Protection Agency concerning air quality in
California’s San Joaquin Valley.
The Clean Air Act delegates authority to the EPA to set
national ambient air quality standards (“NAAQS”). A state
is primarily responsible for maintaining air quality within its
entire geographic area and must submit state implementation
plans (“SIPs”) that specify how NAAQS will be met in each
air quality control region of the state. The EPA designates
regions as “attainment” or “nonattainment” based on
whether they meet the NAAQS.
Section 172(c)(9) of the Act requires that SIPs for
nonattainment areas include contingency measures if the
area fails to make reasonable further progress or fails to meet
a NAAQS by the applicable attainment date. Petitioners
contend that the contingency measures approved by the final
rule fall short of the improvement required for the Valley’s
air quality.
The panel held that the EPA exceeded its authority when
it grafted a feasibility exemption onto Section
172(c)(9). Applying Loper Bright Enters. v. Raimondo, 603
U.S. 369 (2024), the panel held that because the text of
Section 172(c)(9) is ambiguous, it must use statutory
*
This summary constitutes no part of the opinion of the court. It has
been prepared by court staff for the convenience of the reader.
4 COMM. FOR A BETTER ARVIN V. U.S. EPA
interpretation to independently interpret the statute to
determine its most faithful reading. Congress did not
expressly provide that the EPA should consider feasibility in
Section 172(c)(9). The panel held that the EPA erred by
plucking a feasibility exemption out of thin air and reading
it into Section 172(c)(9) when the language of the provision
does not provide for one.
The panel further held that the provision’s directive to
design “specific” contingency measures that shall “take
effect” did not implicitly grant the EPA discretion to
consider feasibility. In addition, permitting a feasibility
exemption for contingency measures undermines both the
specific function of Section 172(c)(9) and the overarching
purpose of the Act.
The panel held that remand without vacatur was the
appropriate remedy given the potential disruptive
consequences of the Valley lacking contingency measures
while the EPA reconsiders the rule.
Dissenting, Judge Bress wrote that the majority’s
interpretation of the Clean Air Act—that California’s
contingency measures do not meet the requirements of
Section 172(c)(9) because any consideration of feasibility is
completely forbidden when it comes to meeting air quality
benchmarks—reflects serious legal error, conflating a
supposedly improper feasibility assessment with what are
merely the statutory requirements for an emissions reduction
measure to qualify as a contingency measure under Section
172(c)(9) of the Clean Air Act.
COMM. FOR A BETTER ARVIN V. U.S. EPA 5
COUNSEL
Colin C. O'Brien (argued) and Tyler B. Szeto, Earthjustice,
San Francisco, California; Brent J. Newell, Law Office of
Brent J. Newell, Petaluma, California; for Petitioners.
Sarah Izfar (argued), Senior Trial Counsel, Environment and
Natural Resources Division; Robert N. Stander, Deputy
Assistant Attorney General; Adam R.F. Gustafson, Acting
Assistant Attorney General; United States Department of
Justice, Washington, D.C.; Yasmin P. Ortiz and Jefferson
Wehling, Attorneys, United States Environmental Protection
Agency, Washington, D.C.; for Respondents.
Corey M. Moffat (argued), Deputy Attorney General;
Jonathan A. Wiener, Acting Supervising Deputy Attorney
General; Rob Bonta, California Attorney General; Office of
the California Attorney General, San Francisco, California;
Isela G. Welz, Assistant District Counsel; Annette A.
Ballatore, District Counsel; San Joaquin Valley Unified Air
Pollution Control District, Fresno, California; for
Intervenors.
Brian S. Tomasovic, Assistant Chief Deputy Counsel;
Kathryn Roberts, Principal Deputy District Counsel;
Barbara Baird, Chief Deputy Counsel; Bayron T. Gilchrist,
General Counsel; Office of the General Counsel, South
Coast Air Quality Management District, Diamond Bar,
California; Kathrine Pittard, District Counsel, Sacramento
Metropolitan Air Quality Management District, Sacramento,
California; Piero C. Dallarda, Best Best & Krieger LLP,
Riverside, California; Ann M. Siprelle, Best Best & Krieger
LLP, Sacramento, California; for Amici Curiae South Coast
Air Quality Management District, Sacramento Metropolitan
Air Quality Management District, Mojave Desert Air
6 COMM. FOR A BETTER ARVIN V. U.S. EPA
Quality Management District, and California Air Pollution
Control Officers Association.
Robyn Wille, First Assistant Attorney General; Rylie
Slaybaugh, Assistant Attorney General II; Laura T. Mehew,
Senior Assistant Attorney General; Kyle Davenport, Senior
Assistant Attorney General II; Shannon Stevenson, Solicitor
General; Natural Resources and Environment Section,
Colorado Office of the Attorney General, Denver, Colorado;
for Amicus Curiae Colorado Department of Public Health
and Environment.
OPINION
MENDOZA, JR., Circuit Judge:
The San Joaquin Valley’s unique bowl-shaped
topography is both a cradle of abundance and home to over
four million Californians. It also has “some of the worst air
quality in the United States.” Comm. for a Better Arvin v.
EPA, 786 F.3d 1169, 1173 (9th Cir. 2015). The Valley has
repeatedly failed to meet the Clean Air Act’s air quality
standards, a reality reflected by the numerous disputes about
emissions regulation in that area that have reached this court.
The Committee for a Better Arvin, Medical Advocates for
Healthy Air, the National Parks Conservation Association,
and the Sierra Club challenge a final rule issued by the
United States Environmental Protection Agency, arguing
that the contingency measures approved by the rule fall far
short of the improvement required for the Valley’s air
quality. We conclude that the EPA exceeded its authority
COMM. FOR A BETTER ARVIN V. U.S. EPA 7
when it grafted a feasibility exemption onto Section
172(c)(9) of the Clean Air Act, and we remand.
I.
A.
Enacted in 1963, the Clean Air Act (“Act”) was designed
to promote air quality improvement through a scheme of
“cooperative federalism.” MacClarence v. EPA, 596 F.3d
1123, 1125 (9th Cir. 2010). In the Act, Congress recognizes
that “air pollution prevention . . . and air pollution control at
its source is the primary responsibility of States and local
governments,” but provides for “[f]ederal financial
assistance and leadership.” 42 U.S.C. § 7401(a).
The Act delegates authority to the EPA to set national
ambient air quality standards (“NAAQS”) for certain air
pollutants. 42 U.S.C. § 7409; Whitman v. Am. Trucking
Ass’ns, 531 U.S. 457, 462 (2001). A state is primarily
responsible for maintaining air quality within its “entire
geographic area,” a responsibility that entails submitting
state implementation plans (“SIPs”) that specify how
NAAQS will be met in each air quality control region of the
state. 42 U.S.C. § 7407(a). Within this framework, the EPA
designates regions as “attainment” or “nonattainment” based
on whether they meet the NAAQS. 42 U.S.C. § 7407(d).
Nonattainment areas are also classified by the severity of
nonattainment—fine particulate matter (“PM2.5”)
nonattainment areas are initially classified as “moderate”
and can be subsequently reclassified as “serious.” 40 C.F.R.
§ 51.1002.
8 COMM. FOR A BETTER ARVIN V. U.S. EPA
Section 172(c)(9)1 of the Act also requires that SIPs for
nonattainment areas include contingency measures:
“specific measures to be undertaken if the area fails to make
reasonable further progress,” or fails to meet a NAAQS by
the applicable attainment date. 42 U.S.C. § 7502(c)(9).
Discussing the Section 172(c)(9) contingency measure
requirement, the house report accompanying the 1990
amendments to the Act states that “[s]uch measures are to
take effect without further action by the State o[r]
Administrator, and are to be adequate to compensate for any
emission reduction shortfall.” H.R. Rep. No. 101-490,
reprinted in Cong. Rsch. Serv., A Legislative History of the
Clean Air Act Amendments of 1990, at 3248 (1993). In this
regard, these contingency measures function as a “backup”
in case existing measures fall short. Ass’n of Irritated
Residents v. EPA, 10 F.4th 937, 947 (9th Cir. 2021).
B.
The challenged rule approves two SIP submissions
designed to meet three contingency measure requirements
for the Valley. Petitioners argue that the rule violates the
Act by applying a new, lowered progress standard for
contingency measures and reading a feasibility exemption
into the statute. The EPA maintains that it has applied the
best interpretation of the Act’s requirements for contingency
measures.
The San Joaquin Valley Unified Air Pollution Control
District (“District”) is primarily responsible for developing
plans to provide for the Valley’s attainment of NAAQS. It
works with the California Air Resources Board (“CARB”)
to develop those plans. In June 2023, CARB submitted two
1
Section 172(c)(9) of the Act is codified at 42 U.S.C. § 7502(c)(9).
COMM. FOR A BETTER ARVIN V. U.S. EPA 9
SIPs to the EPA addressing PM2.5 and precursor pollutants,
including nitrogen oxides (“NOx”), in the Valley. 2 They
contained three contingency measures designed to
collectively meet the contingency measure requirements for
the 1997 annual, 2006 24-hour, and 2012 annual PM2.5
standards.3
One of these contingency measures would require
stricter wood burning restrictions if triggered, the second
would require more “fugitive dust” control measures in
certain open areas in the Valley, and the third would require
more vehicles in the area to undergo smog checks. Notably,
the proposed rule required only “one year’s worth of
progress.” This marked a departure from the EPA’s
traditional requirement that contingency measures provide
for “one year’s worth of reasonable further progress.”
The proposed rule also recommended accepting
“feasibility analyses” provided by CARB and the District to
justify the emissions reductions for precursor pollutant NOx
falling short of that lowered “progress” standard. It detailed
CARB and the District’s analyses of “contingency measure
opportunities,” including CARB’s arguments on
technological limitations and time pressure. Accepting the
professed infeasibility of additional contingency measures
paved the way for the EPA to approve the SIPs, despite the
fact that the contingency measures fell significantly short of
2
PM2.5 is fine particulate matter with a diameter of 2.5 micrometers or
less. NOx is a precursor pollutant that causes the formation of PM2.5.
3
The EPA classified the San Joaquin Valley as a serious nonattainment
area for the 1997 annual PM2.5 standard in 2015, as a serious
nonattainment area for the 2006 24-hour PM2.5 standard in 2016, and as
a serious nonattainment area for the 2012 annual PM2.5 standard in
2021.
10 COMM. FOR A BETTER ARVIN V. U.S. EPA
required NOx emissions reductions, even under the lowered
one year’s worth of progress standard.
Environmental advocacy groups raised numerous
concerns about the proposed rule in the subsequent notice-
and-comment period. The groups characterized the rule as
an attempt by the EPA to “completely abdicate its obligation
to require meaningful contingency measures” by
abandoning its longstanding interpretation of Section
172(c)(9) as requiring one year’s worth of reasonable further
progress. They further criticized the rule’s inclusion of a
feasibility demonstration which further lowers the progress
required from contingency measures. On this point, they
argued that such feasibility demonstrations contradict the
“plain language” of the Act, which does not apply any
feasibility standard to contingency measures.
Despite these concerns, the EPA issued the final rule
with the lowered progress standard and the feasibility
demonstration intact. The rule acknowledged the EPA’s
“long-standing approach” of requiring one year’s worth of
reasonable further progress, but it argued that that standard
was “unnecessarily conservative.” And it defended further
lowering progress requirements for contingency measures in
certain circumstances:
[A]s stated in our proposed rule and the
EPA’s Draft Revised Contingency Measures
Guidance, where a state is unable to identify
contingency measures that would provide
approximately [one year’s worth] of emission
reductions, the state should provide a
reasoned justification (referred to herein as
an “infeasibility demonstration”) that
explains and documents how it has evaluated
COMM. FOR A BETTER ARVIN V. U.S. EPA 11
all existing and potential control measures
relevant to the appropriate source categories
and pollutants in the nonattainment
area and has reached reasonable conclusions
regarding whether such measures are
feasible.
II.
The contingency measures create sufficient emission
reductions for direct PM2.5 emissions to meet the EPA’s
longstanding one year’s worth of reasonable further progress
standard. But NOx emission reductions fall short of both
one year’s worth of reasonable further progress and the
rule’s lowered progress standard. The final rule reasons that
the approved contingency measures nevertheless satisfy
Section 172(c)(9) because CARB and the District provided
“reasoned justifications for not adopting additional
contingency measures.” So this challenge turns on whether
Section 172(c)(9) allows the EPA to exempt contingency
measures from progress standards if the air agency makes a
feasibility demonstration.4 We find that it does not.
A.
Under the general standard set by Section 706 of the
Administrative Procedure Act, the court sets aside an agency
action if it is “arbitrary, capricious, an abuse of discretion, or
otherwise not in accordance with the law.” 5 U.S.C.
§ 706(2)(A); see also Sierra Club v. EPA, 671 F.3d 955, 961
(9th Cir. 2012) (applying this general standard because the
4
We neither endorse nor reject the EPA’s use of “one year’s worth of
progress” instead of the longstanding one year’s worth of reasonable
further progress standard because this petition rises and falls on
feasibility.
12 COMM. FOR A BETTER ARVIN V. U.S. EPA
Act does not specify a standard for SIP approvals). “Section
706 makes clear that agency interpretations of statutes . . .
are not entitled to deference.” Loper Bright Enters. v.
Raimondo, 603 U.S. 369, 392 (2024).
Until recently, we would have deferred to the EPA’s
reasonable interpretation of ambiguous statutory language,
even if it was not the only permissible construction. See
Chevron, U.S.A., Inc. v. Nat. Res. Def. Council, Inc., 467
U.S. 837, 843 (1984), overruled by, Loper Bright, 603 U.S.
at 412. But the Supreme Court now instructs courts to use
their “full interpretive toolkit” to find the “best meaning” of
ambiguous statutes rather than deferring to agency
interpretations. Loper Bright, 603 U.S. at 408–09. Because
the text of Section 172(c)(9) is ambiguous,5 we must dust off
our well-worn tools of statutory interpretation to
independently interpret the statute and to determine its most
faithful reading.
B.
The text of Section 172(c)(9) is silent on feasibility. To
support the EPA’s contention that feasibility demonstrations
are nonetheless allowed by the provision, the challenged rule
emphasizes that “the statutory provisions applicable to other
nonattainment area plan control measure requirements . . .
allow air agencies to exclude certain control measures that
are deemed unreasonable or infeasible.” In other words, the
EPA’s position is that explicit feasibility allowances
elsewhere in the Act suggest that it can consider feasibility
in this instance. But the fact that other provisions in the Act
5
“A statute is ambiguous if it gives rise to more than one reasonable
interpretation.” Woods v. Carey, 722 F.3d 1177, 1181 (9th Cir. 2013)
(citation modified).
COMM. FOR A BETTER ARVIN V. U.S. EPA 13
provide for infeasibility exemptions—and that Section
172(c)(9) does not—fatally undermines the EPA’s position.
“Congress generally acts intentionally when it uses
particular language in one section of a statute but omits it in
another.” Dep’t of Homeland Sec. v. MacLean, 574 U.S.
383, 391 (2015). As the Supreme Court observed in an early
Clean Air Act case, “[w]here Congress intended the
Administrator to be concerned about economic and
technological infeasibility, it expressly so provided.” Union
Elec. Co. v. EPA, 427 U.S. 246, 257 n.5 (1976). And
Congress has provided for feasibility considerations
elsewhere in the Act.
Section 112 directs the EPA to promulgate and enforce
emissions standards to control certain hazardous air
pollutants, but it provides that “if it is not feasible in the
judgment of the Administrator to prescribe or enforce an
emission standard for control of a hazardous air pollutant or
pollutants, the Administrator may” promulgate other
“design, equipment, work practice, or operational
standard[s]” to meet the provision’s goals. 42 U.S.C.
§ 7412(h)(1) (emphasis added).
Then Section 188(e) of the Act permits attainment date
extensions for serious PM10 nonattainment areas if the state
can show that “the plan for that area includes the most
stringent measures that are included in the implementation
plan of any State or are achieved in practice in any State, and
can feasibly be implemented in the area.” 42 U.S.C.
§ 7513(e) (emphasis added). It also expressly permits the
consideration of “the technological and economic feasibility
of various control measures.” Id. (emphasis added).
Section 202, which covers motor vehicle emissions, also
makes several feasibility allowances. It provides that
14 COMM. FOR A BETTER ARVIN V. U.S. EPA
regulations cannot go into effect until “it would be feasible
to implement” them, requiring collaboration with the
National Academy of Sciences to “conduct a comprehensive
study and investigation of the technological feasibility of
meeting” certain emissions standards required by the
provision, and allowing the Administrator to adjust
standards related to the “useful life” of vehicles and engines
“if he determines that it is feasible for vehicles and engines
subject to such standards to meet such standards for a longer
useful life.” 42 U.S.C. § 7521(a)(5)(B), (c)(1), (j)(3)
(emphases added).
As in Department of Homeland Security v. MacLean, the
interpretive canon that Congress acts deliberately by
omitting language that is included elsewhere in a statute
“applies with particular force here.” 574 U.S. at 392.
Feasibility is expressly referenced numerous times
throughout the Act and the term appears “in close proximity”
to Section 172(c)(9). Id. Even elsewhere in Section 172,
there is language providing that the Administrator can
consider the “availability and feasibility of the pollution
control measures” when classifying nonattainment areas and
extending attainment dates. See 42 U.S.C.
§§ 7502(a)(1)(A), (a)(2)(A) (emphasis added). But there is
no such language in Section 172(c)(9).
Congress did not expressly provide that the EPA should
consider feasibility in Section 172(c)(9). It easily could have
done so. Indeed, it has done so elsewhere in the Act. The
EPA erred by plucking a feasibility exemption out of thin air
and reading it into Section 172(c)(9) when the language of
the provision does not provide for one. So the challenged
rule is contrary to the Act’s best meaning and must be
remanded to the EPA.
COMM. FOR A BETTER ARVIN V. U.S. EPA 15
III.
The EPA also argues that Congress granted it
“discretionary authority to consider feasibility” by stating in
Section 172(c)(9) that contingency measures are “specific
measures” that will “take effect” without any qualifying
language. But the hazy language of Section 172(c)(9) does
not automatically give the EPA the right to consider
feasibility. The Supreme Court has specifically rejected the
presumption “that statutory ambiguities are implicit
delegations to agencies.” Loper Bright, 603 U.S. at 399. So
we must determine whether the best reading of the
provision’s directive to design “specific” contingency
measures that shall “take effect” implicitly grants the EPA
discretion to consider feasibility. We find that it does not.
A.
On this point, Union Electric is instructive. There, the
Supreme Court considered whether the “operator of a
regulated emission source” could “raise the claim that it is
economically or technologically infeasible to comply with
the plan.” Union Elec., 427 U.S. at 249. The petitioner, an
electric utility company, argued that a provision of the Act
required consideration of technological and economic
infeasibility because it provided that air quality standards be
met “as expeditiously as practicable,” and within a
“reasonable time.” Union Elec., 427 U.S. at 257–58. The
petitioner asserted that “what is ‘practicable’ or ‘reasonable’
cannot be determined without assessing whether what is
proposed is possible.” Id. at 258.
The Supreme Court soundly rejected the petitioner’s
argument, reasoning that the Act set strict compliance
requirements that were “expressly designed to force
regulated sources to develop pollution control devices that
16 COMM. FOR A BETTER ARVIN V. U.S. EPA
might at the time appear to be economically or
techno[logically] infeasible.” Id. at 257. The Court went as
far as concluding that “Congress intended claims of
economic and technological infeasibility to be wholly
foreign to the Administrator’s consideration of a state
implementation plan.” Id. at 256. The Court cited senators’
remarks during the legislative process, including Senator
Edmund Muskie’s statement that Congress was responsible
for protecting public health, which “may mean that people
and industries will be asked to do what seems to be
impossible at the present time.” Id. at 258–59 (citation
modified).
While this petition concerns a different provision of the
Act, Union Electric’s rationale nevertheless applies.6 The
contested statutory language in Union Electric required
evaluation of what time frames would be “reasonable” or
“practicable.” Even that was not enough to allow for
feasibility considerations that were not explicitly provided
for in the statute. In contrast, Section 172(c)(9) is devoid of
references to practicability, and the EPA points only to
“specific measures to be undertaken” as evidence that
Congress intended to provide discretion to consider
feasibility. In other words, if the phrases “as expeditiously
as practicable,” and “within a reasonable time” do not permit
consideration of feasibility, it is difficult to see how “specific
6
The dissent spills much ink arguing that Union Electric is
distinguishable from this petition for review. This argument misses the
point of our analysis. It was never our contention that Union Electric
was factually or procedurally identical to this case. Union Electric is an
early example of the Supreme Court refusing to “read in” technological
and economic infeasibility considerations into the Act when Congress
did not expressly include them.
COMM. FOR A BETTER ARVIN V. U.S. EPA 17
measures to be undertaken,” a phrase even further
disconnected from feasibility, would allow it.
B.
Department of Treasury, IRS v. FLRA is also instructive.
494 U.S. 922 (1990). In that case, the Supreme Court
rejected the government’s argument that the term
“applicable laws” in one provision of the Civil Service
Reform Act of 1978 was equivalent to the phrase “any law,
rule, or regulation,” which is used elsewhere in the statute.
Id. at 931–33. The majority reasoned that a “statute that in
one section refers to ‘law, rule or regulation,’ and in another
section to only ‘laws’ cannot, unless we abandon all pretense
at precise communication, be deemed to mean the same
thing in both places.” Id. at 932.
If we hold that “specific measures to be undertaken”
means “feasibility,” a term that is used throughout the Act
and which holds a particular meaning, then we will be
choosing to “abandon all pretense at precise
communication,” as the Supreme Court warned against in
Department of Treasury. Reading a feasibility standard into
a provision whose text plainly does not provide for one
would undermine the clarity of the Act’s language and usurp
Congress’s choices in favor of an agency’s preference. As
discussed supra, Congress is perfectly capable of writing
feasibility into statutory language; it has done so repeatedly
throughout the Act. So we find that Congress did not
implicitly grant the EPA discretion to consider feasibility
with the language of Section 172(c)(9).
IV.
Turning to another tool in our statutory interpretation
toolbox, “[i]t is a fundamental canon of statutory
18 COMM. FOR A BETTER ARVIN V. U.S. EPA
construction that the words of a statute must be read in their
context and with a view to their place in the overall statutory
scheme.” West Virginia v. EPA, 597 U.S. 697, 721 (2022)
(quoting Davis v. Mich. Dep’t of Treasury, 489 U.S. 803,
809 (1989)). “[W]e must interpret statutes as a whole,
giving effect to each word and making every effort not to
interpret a provision in a manner that renders other
provisions of the same statute inconsistent, meaningless or
superfluous.” Boise Cascade Corp. v. EPA, 942 F.2d 1427,
1432 (9th Cir. 1991).
“By requiring contingency measures, the Act closes any
potential gap in progress should a nonattainment area miss a
milestone.” Ass’n of Irritated Residents, 10 F.4th at
942. The feasibility demonstrations approved by this rule
effectively allow states to eliminate that statutory imperative
on demand. Accepting such demonstrations is particularly
harmful to the purpose of contingency measures because the
EPA’s guidance anticipates that these demonstrations will
allow for a substantial lowering of progress standards. The
EPA has stated that “[w]ith sufficient justification,
[contingency measures] representing a small amount of
reductions may be reasonable.”
Lowering or largely eliminating progress standards for
Section 172(c)(9) contingency measures undermines their
role in the Act’s overall statutory scheme. To maintain
contingency measures’ function as a “plan B,” 7 they should
7
The dissent suggests that our use of the phrase “plan B” indicates a
larger misunderstanding of contingency measures’ purpose. But whether
we say “plan B” or some other term, contingency measures’ function as
a backup should not be discounted. As we have explained, “the reason
the statute requires contingency measures is to have a backup that can be
put in place immediately in case already-implemented measures in a plan
fail to achieve reasonable further progress. The agency may not avoid
COMM. FOR A BETTER ARVIN V. U.S. EPA 19
be designed to compel a nonattainment area to meet a
consistent standard of progress. 8 Reading feasibility
demonstrations into Section 172(c)(9), which does not
provide for them, undermines that function.
V.
We end our analysis with statutory purpose. It is a
“familiar canon of statutory construction that remedial
legislation should be construed broadly to effectuate its
purposes.” Tcherepnin v. Knight, 389 U.S. 332, 336
(1967). “The overriding purpose of the Clean Air Act is to
force the states to do their job in regulating air pollution
effectively so as to achieve baseline air quality standards, the
NAAQS.” Exxon Mobil Corp. v. EPA, 217 F.3d 1246, 1255
(9th Cir. 2000). As Congressman Bob Carr stated during the
legislative debate of the 1990 amendments, “[u]ltimately,
the purpose of the Clean Air Act is to improve the public’s
health through a cleaner environment.” House Debate on
the Clean Air Act Amendments of 1990 Conference Report,
reprinted in Cong. Rsch. Serv., A Legislative History of the
Clean Air Act Amendments of 1990, at 1342 (1993).
Section 172 of the Act furthers those goals of effective
regulation and public health by setting general requirements
for nonattainment areas. See 42 U.S.C. § 7502. Those
requirements include nonattainment plans that “require
reasonable further progress,” and contingency measures that
pick up the slack if those nonattainment plans fail to meet
the need for robust contingency measures by assuming that they will not
be needed.” Ass’n of Irritated Residents v. EPA, 10 F.4th 937, 947 (9th
Cir. 2021) (citation modified).
8
Again, we take no position as to whether that consistent standard should
be one year’s worth of reasonable further progress or one year’s worth
of progress.
20 COMM. FOR A BETTER ARVIN V. U.S. EPA
the reasonable-further-progress standard. Id. at §§ (c)(2),
(9). Contingency measures are required by the Act with the
purpose of bringing nonattainment areas in line with PM2.5
NAAQS. Permitting a feasibility exemption for these
contingency measures undermines both the specific function
of Section 172(c)(9) and the overarching purpose of the Act.
VI.
This case is about a limited question of statutory
interpretation: does the best meaning of Section 172(c)(9)
include a feasibility exemption, even if the text does not
expressly provide for one? The answer, based on our
established canons of statutory interpretation, is no.
The dissent extensively discusses policy concerns. It
warns that this decision will lead to “regulatory freefall” and
a “treacherous trail.” First, we will note that it is unlikely
that this limited statutory interpretation decision will bring
about an administrative law apocalypse. It is worth
reiterating that the EPA, not the petitioners, is proposing a
new path. Our decision not to allow a novel feasibility
analysis maintains the status quo.
The dissent suggests that we should discuss the
“actual feasibility analyses,” and stresses that the EPA’s
analysis is “173 single-spaced pages.” We do not discuss the
depth of the feasibility analyses because that has no bearing
on the best meaning of the statutory provision at issue. The
thoroughness of the EPA’s individual feasibility analyses
does not ex post facto justify reading a feasibility exemption
into Section 172(c)(9). To consider that would be to
improperly broaden the scope of our analysis. This is a
statutory interpretation question. No more, no less.
COMM. FOR A BETTER ARVIN V. U.S. EPA 21
Much of the dissent’s argument boils down to the idea
that we should make Section 172(c)(9) mean what the EPA
and air quality districts say it should mean—and if we don’t,
catastrophe will ensue. But we will not warp our statutory
interpretation to reach a predetermined conclusion.
However sincerely held the dissent’s concerns may be, we
cannot substitute policy goals for neutral statutory
interpretation. It is the prerogative of Congress, not this
court, to amend legislation based on policy concerns. In the
post-Chevron era, we are tasked with employing our “full
interpretive toolkit” to find the “best meaning” of ambiguous
statutes, without deferring to agency interpretations. Loper
Bright, 603 U.S. at 408–09. We have done so.
VII.
Having concluded that the challenged rule violates the
Act, we must now determine the appropriate remedy.
Petitioners request that this court “remand[] the EPA’s
approval” of the contingency measures so that “California
will need to revisit its decision[-]making and adopt
meaningful control measures in compliance with the Clean
Air Act.” They also seek an award of litigation costs,
including attorney’s fees. They do not request vacatur.
“The traditional remedy for erroneous administrative
decisions is vacatur, but we will leave invalid agency action
in place when equity demands that we do so.” Migrant
Clinicians Network v. EPA, 88 F.4th 830, 847 (9th Cir. 2023)
(citation modified). The Ninth Circuit employs a two-factor
balancing test to determine whether an agency action should
stay in effect on remand—weighing the severity of the
agency’s errors against “the disruptive consequences of an
interim change that may itself be changed.” Cal. Cmtys.
Against Toxics v. EPA, 688 F.3d 989, 992 (9th Cir. 2012)
22 COMM. FOR A BETTER ARVIN V. U.S. EPA
(quoting Allied–Signal, Inc. v. U.S. Nuclear Regul. Comm’n,
988 F.2d 146, 150–51 (D.C. Cir. 1993)); Migrant Clinicians
Network, 88 F.4th at 848. Evaluating agency error includes
considering whether “vacating a faulty rule could result in
possible environmental harm.” Pollinator Stewardship
Council v. EPA, 806 F.3d 520, 532 (9th Cir. 2015).
Petitioners have not requested vacatur, and we find that
remand alone is appropriate given the potential disruptive
consequences of the Valley lacking contingency measures
while the EPA reconsiders this rule. So we remand without
vacatur.
As for costs, the Act provides that “[i]n any judicial
proceeding under this section, the court may award costs of
litigation (including reasonable attorney and expert witness
fees) whenever it determines that such award is
appropriate.” 42 U.S.C. § 7607(f). We find that such an
award is appropriate in this case.
REMANDED.
COMM. FOR A BETTER ARVIN V. U.S. EPA 23
BRESS, Circuit Judge, dissenting:
The majority opinion holds that Section 172(c)(9) of the
Clean Air Act, 42 U.S.C. § 7502(c)(9), requires States to
adopt technologically and economically infeasible
contingency measures for meeting air quality benchmarks.
This alarming ruling is mistaken, sending States into a
regulatory freefall in which they must either adopt infeasible
emission control measures or else face severe, escalating
sanctions. California and the federal government do not
always see eye to eye, but they both agree the Clean Air Act
was never meant to operate in this Kafkaesque way.
In this case, California and the EPA exhaustively
explained why further contingency measures beyond the
ones California has adopted do not meet the requirements of
Section 172(c)(9) because they could not take effect
automatically and yield emissions reductions promptly—
precisely the analysis that Section 172(c)(9) requires. The
majority takes issue with none of these extensive findings.
Nor does it point to other possible contingency measures that
California and the EPA failed to consider. Instead,
California’s contingency measures fail because any
consideration of feasibility is completely forbidden when it
comes to meeting these air quality benchmarks. That
interpretation of the Clean Air Act reflects serious legal
error, conflating a supposedly improper feasibility
assessment with what are merely the statutory requirements
for an emissions reduction measure to qualify as a
contingency measure under Section 172(c)(9). Because the
majority rests on a fundamental misapprehension of the
statutory scheme and puts States in an untenable
stranglehold, I must respectfully dissent.
24 COMM. FOR A BETTER ARVIN V. U.S. EPA
I
A
Before turning to the facts of this case, I begin with an
explanation of how Section 172(c)(9) contingency measures
fit into the broader Clean Air Act apparatus, which is
important in understanding where the majority goes wrong.
To protect public health, the Clean Air Act instructs the
EPA to establish national ambient air quality standards
(NAAQS) for various pollutants. See EPA v. EME Homer
City Generation, L.P., 572 U.S. 489, 498 (2014); see 42
U.S.C. § 7409(a); 40 C.F.R. § 50.7(a). If a region meets
NAAQS for a given pollutant, the EPA classifies that region
as “attainment.” 42 U.S.C. § 7407(d)(1)(A)(ii). If a region
does not meet NAAQS, the EPA classifies it as
“nonattainment” and sets a deadline by which the region
must reach compliance. Id. §§ 7407(d)(1)(A)(i), 7502(a).
Under the Act, “[t]here are several degrees of nonattainment,
ranging from marginal to extreme, and each classification
imposes increasingly stringent requirements to reduce
emissions and promote progress toward attainment.” Ass’n
of Irritated Residents v. EPA, 10 F.4th 937, 942 (9th Cir.
2021) (citations omitted). For fine particulate matter, the
pollutant at issue here, nonattainment areas are initially
classified as “moderate” and are reclassified as “serious” if
the EPA finds that the area failed to attain the NAAQS by
the moderate-area attainment date. 40 C.F.R. § 51.1002(a),
(b)(2).
When a region is designated “nonattainment” for a given
pollutant, the state must create a State Implementation Plan
(SIP), which the EPA must approve. See Bahr v. Regan, 6
F.4th 1059, 1065 (9th Cir. 2021); 42 U.S.C. §§ 7410,
7502(b). “Each SIP must include enforceable emission
COMM. FOR A BETTER ARVIN V. U.S. EPA 25
limitations and other control measures necessary to attain
the NAAQS, as well as timetables for compliance.”
Bayview Hunters Point Cmty. Advocs. v. Metro. Transp.
Comm’n, 366 F.3d 692, 695 (9th Cir. 2004), as amended on
denial of reh’g and reh’g en banc (June 2, 2004). The SIP
must “provide for the implementation