Medical Advocates for Healthy v. Usepa ( 2022 )


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  •                                                                               FILED
    NOT FOR PUBLICATION
    APR 13 2022
    UNITED STATES COURT OF APPEALS                         MOLLY C. DWYER, CLERK
    U.S. COURT OF APPEALS
    FOR THE NINTH CIRCUIT
    MEDICAL ADVOCATES FOR                            No.   20-72780
    HEALTHY AIR; NATIONAL PARKS
    CONSERVATION ASSOCIATION;                        EPA Nos.
    ASSOCIATION OF IRRITATED                         EPA-R09-OAR-2019-0318
    RESIDENTS; SIERRA CLUB,                          FRL-10011-44-Region 9
    Petitioners,
    MEMORANDUM*
    v.
    U.S. ENVIRONMENTAL PROTECTION
    AGENCY; ANDREW WHEELER,
    Administrator, U.S. Environmental
    Protection Agency; JOHN BUSTERUD,
    Regional Administrator, Region IX, U.S.
    Environmental Protection Agency,
    Respondents,
    ______________________________
    SAN JOAQUIN VALLEY UNIFIED AIR
    POLLUTION CONTROL DISTRICT,
    Intervenor.
    On Petition for Review of an Order of the
    Environmental Protection Agency
    *
    This disposition is not appropriate for publication and is not precedent
    except as provided by Ninth Circuit Rule 36-3.
    Argued and Submitted February 11, 2022
    San Francisco, California
    Before: WARDLAW, IKUTA, and BADE, Circuit Judges.
    Petitioners seek review of a final rule issued by the Environmental
    Protection Agency (the EPA) under the Clean Air Act (the CAA), 
    85 Fed. Reg. 44,192
    -01 (July 22, 2020), approving an attainment plan (the “2018 Plan”)
    submitted by California and adopted by both the San Joaquin Valley Unified Air
    Pollution Control District (the “District”) and the California Air Resources Board
    (CARB) to meet the 2006 24-hour PM2.5 national ambient air quality standards
    (NAAQS) in the San Joaquin Valley.1 The final rule also approved California’s
    request to extend the attainment date for meeting these standards from December
    31, 2019 to December 31, 2024.
    Petitioners argue that the EPA’s approval was arbitrary and capricious
    because: (1) the 2018 Plan’s aggregate commitments did not satisfy applicable
    requirements, and (2) the EPA’s analysis regarding implementation of the best
    available control measures (“BACM”) and most stringent measures (“MSM”) was
    1
    PM2.5 means particles measuring less than 2.5 microns in diameter. PM2.5
    may form due to the emissions of other chemicals such as nitrogen oxides (NOx).
    See 
    85 Fed. Reg. 17,382
     (Mar. 27, 2020).
    2
    arbitrary and capricious, such that the attainment deadline extension should not
    have been granted.
    We first consider petitioners’ challenges to the 2018 Plan’s aggregate
    commitments, involving the use of incentive-based control measures to achieve
    specified reductions of emissions according to a schedule. To the extent
    petitioners argue that the EPA’s approval of aggregate commitments in the 2018
    Plan is illegal because such commitments allow states to impermissibly defer plan
    development, we reject this argument. We have previously concluded that the
    EPA may reasonably rely on a control strategy that includes aggregate
    commitments, and that such an approach does not violate the CAA. See Comm. for
    a Better Arvin v. EPA, 
    786 F.3d 1169
    , 1179 (9th Cir. 2015); see also 
    42 U.S.C. § 7410
    (a)(2)(A) (providing that a state implementation plan may include
    “schedules and timetables for compliance”). We also reject petitioners’ argument
    that the aggregate commitments are invalid on the grounds that they are
    unenforceable. Upon the EPA’s approval of the aggregate commitments as part of
    the 2018 Plan, they become federally enforceable requirements of an applicable
    implementation plan, which can be enforced by the public and the EPA. See 
    42 U.S.C. §§ 7602
    (q), 7604(a)(1), 7413(a)(1); see also Arvin, 786 F.3d at 1180.
    Petitioners’ reliance on 42 U.S.C. §§ 7511a(e)(5) and 7410(k)(4) to support their
    3
    argument that aggregate commitments are precluded by the CAA is misplaced.
    The CAA’s inclusion of § 7511a(e)(5), which allows the EPA to approve
    provisions of an implementation plan in certain ozone nonattainment areas “which
    anticipate development of new control techniques or improvement of existing
    control technologies,” does not prevent the EPA from approving a plan such as the
    one here, which neither relies on anticipated developments in technology nor
    involves an ozone nonattainment area. Nor does § 7410(k)(4), which allows the
    EPA to “approve a plan revision based on a commitment of the State to adopt
    specific enforceable measures by a date certain,” prevent the EPA from approving
    a state’s aggregate commitments as part of a larger plan. See 85 Fed. Reg. at
    44,204.
    Petitioners next challenge the EPA’s application of its traditional three-
    factor test for evaluating the permissibility of aggregate commitments. Under this
    established test, the EPA considers: (1) whether the commitment addresses a
    limited portion of the statutorily required program; (2) whether the state is capable
    of fulfilling its commitment; and (3) whether the commitment is for a reasonable
    and appropriate period of time. See 
    75 Fed. Reg. 74,518
    -01, 74,535–36; see also
    BCCA Appeal Grp. v. EPA, 
    355 F.3d 817
    , 840 (5th Cir. 2003). We conclude that
    4
    the EPA reasonably determined that the first and third factor were met, but erred in
    concluding that the second factor was met.
    First, the EPA reasonably determined that the commitment addressed a
    limited portion of the statutorily-required program in light of “the facts and
    circumstances of the nonattainment area at issue.” 85 Fed. Reg. at 44,198.
    Petitioners argue that the EPA erred in allowing California to make aggregate
    commitments to address 17 to 31 percent of the emissions reductions, because
    historically the EPA had approved aggregate commitments that addressed
    approximately 10 percent of the emissions to be reduced. We reject this argument
    because petitioners fail to identify any statutory or regulatory authority precluding
    the EPA from allowing aggregate commitments to address a portion of total
    emission reductions larger than 10 percent, and because the petitioners fail to
    otherwise establish that the EPA’s approval of higher percentages in this case was
    so unreasonable as to be arbitrary and capricious. See Bahr v. EPA, 
    836 F.3d 1218
    ,
    1228 (9th Cir. 2016) (“[The arbitrary and capricious] standard is ‘highly
    deferential, presuming the [EPA’s] action to be valid and affirming the agency
    action if a reasonable basis exists for its decision.’” (citation omitted)).
    Second, the EPA reasonably determined that the aggregate commitments
    were for a reasonable and appropriate period of time, therefore satisfying the third
    5
    factor of the three-factor test. Although the record shows that the District intends
    to implement certain measures after January 1, 2024, the date by which California
    must achieve its commitments, the EPA points out that the 2018 Plan does not rely
    on these measures to demonstrate attainment. Petitioners do not affirmatively
    dispute this point. Thus, the EPA’s approval of the time period for the aggregate
    commitments is not arbitrary or capricious.
    Petitioners also argue that the aggregate commitments did not satisfy the
    second factor of the three-factor test—whether the state is capable of fulfilling its
    commitments—because California is unable to adequately fund the Plan’s
    incentive-based control measures. We agree with this argument. Based on
    CARB’s own calculations, there is a potential $2.6 billion shortfall in funding for
    the incentive-based measures, which could result in emission reduction shortfalls
    of approximately 7% of the total NOx reductions and 8% of the total PM2.5
    reductions necessary for attainment. See 85 Fed. Reg. at 44,201. The EPA fails to
    provide evidence or reasoned explanation for its conclusion that California will be
    able to fulfill its commitment despite this shortfall. Instead, the EPA speculates
    that circumstances may arise in the future that will allow the state to do so.
    Specifically, the EPA asserts (1) that its own analysis indicates the funding
    shortfall may be closer to $2 billion as opposed to $2.6 billion, see id., and the
    6
    actual funding shortfall may be even smaller, (2) that certain emission reduction
    measures might be less expensive to implement than the state currently predicts,
    (3) that certain yet-to-be-quantified sources of emission reductions in the 2018
    Plan might make up for shortfalls in emission reductions caused by lack of
    funding, and finally, (4) that California and the District may identify other
    measures in the future to fulfill the commitments. Because these speculative
    assertions are unsupported by evidence, they fail to ensure that California and the
    District have a plausible strategy for achieving this portion of the attainment
    strategy, and therefore do not collectively satisfy the second factor of the EPA’s
    three-factor test. See also 
    42 U.S.C. § 7410
    (a)(2)(E) (requiring, inter alia, that
    state implementation plans provide necessary assurances of adequate funding for
    carrying out the plan). Therefore, we conclude that this portion of the EPA’s
    analysis is arbitrary and capricious because there is no “rational connection
    between the facts found” by the EPA regarding the funding shortfall and the EPA’s
    conclusion that the District will nevertheless meet the attainment goals. Barnes v.
    U.S. Dep’t of Transp., 
    655 F.3d 1124
    , 1132 (9th Cir. 2011).
    Having addressed petitioners’ challenges relating to the EPA’s approval of
    the aggregate commitments, we now turn to petitioners’ argument that the state
    failed to meet BACM and MSM requirements, and that the EPA’s approval of the
    7
    request for a five-year extension was therefore arbitrary and capricious on that
    ground. We conclude that the EPA undertook a rigorous analysis of compliance
    with BACM and MSM requirements in granting the five-year extension. See 
    42 U.S.C. § 7513
    (e). We reject petitioners’ arguments to the contrary.
    We first reject petitioners’ argument that the EPA cannot evaluate the
    stringency of control measures in the aggregate, but must evaluate each control
    measure individually to ensure each is the most stringent available. That is, we
    defer to the EPA’s reasonable conclusion that it can apply a holistic MSM analysis
    when the rule as a whole is as or more stringent than any analogous rule in other
    jurisdictions. Petitioners have not pointed to any provision precluding such an
    approach or requiring the EPA to conduct an individualized MSM analysis for each
    control measure. For similar reasons, we also reject petitioners’ argument that the
    EPA erred in using different levels of generality to evaluate the stringency of
    control measures, because the petitioners cite no legal authority preventing the
    EPA from doing so. The EPA’s thorough analysis provided a sufficient
    explanation to support its conclusion.
    We reject petitioners’ argument that Rule 4901 of the 2018 Plan is not
    sufficiently stringent because the rule involves implementing relevant measures in
    some areas of the San Joaquin Valley and not others. The EPA reasonably
    8
    determined that this type of targeted approach is acceptable provided the rule as a
    whole is as or more stringent than any analogous rule in other jurisdictions. As the
    EPA determined, and as petitioners do not affirmatively dispute, Rule 4901 results
    “in greater emission reductions than the provisions of any other analogous rule.”
    Therefore, petitioners fail to demonstrate the EPA’s conclusion was arbitrary and
    capricious.
    Petitioners’ argument that the EPA failed to adequately consider increased
    building electrification requirements also fails, because the EPA considered such
    an approach and reasonably accepted the state’s determination that it was not
    feasible at this time.
    Finally, we reject petitioners’ argument that the EPA was unreasonable in
    approving the District’s Rule 4550 “menu” approach to controlling dust emissions
    from agricultural sources—i.e., allowing the regulated community to choose
    among various control measures—because such an approach is not sufficiently
    stringent. We have previously upheld the approval of such an approach as a
    “common and accepted practice for the control of dust . . . [especially] because of
    the variable nature of farming.” See Vigil v. Leavitt, 
    381 F.3d 826
    , 837 (9th Cir.
    2004) (citation omitted).
    9
    Accordingly, we vacate the portion of the final rule that determined that the
    relevant aggregate commitments satisfied the second factor of the three-factor test
    and remand to the EPA for further consideration of the second factor, and for
    further proceedings consistent with this decision. See also 
    42 U.S.C. § 7410
    (a)(2)(E). In all other respects, the petition is denied. See Vigil, 
    381 F.3d at 847
    .
    PETITION GRANTED IN PART AND DENIED IN PART.2
    2
    Each party will bear its own costs.
    10
    

Document Info

Docket Number: 20-72780

Filed Date: 4/13/2022

Precedential Status: Non-Precedential

Modified Date: 4/13/2022