Sierra Club et al v. Regina McCarthy
Filing
162
ORDER GRANTING JOINT MOTION TO APPROVE AND ENTER CONSENT DECREE AND DENYING OTHER MOTIONS AS MOOT 120 149 (Illston, Susan) (Filed on 3/2/2015)
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UNITED STATES DISTRICT COURT
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NORTHERN DISTRICT OF CALIFORNIA
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SIERRA CLUB, et al.,
Case No. 13-cv-03953-SI
Plaintiffs,
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v.
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REGINA MCCARTHY, in her official
capacity as Administrator of the United
States Environmental Protection Agency,
ORDER GRANTING JOINT MOTION
TO APPROVE AND ENTER CONSENT
DECREE AND DENYING OTHER
MOTIONS AS MOOT
Re: Dkt. Nos. 120, 149
United States District Court
Northern District of California
Defendant.
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Now before the Court is the parties’ joint motion to approve and enter a proposed consent
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decree, as well as objections thereto. For the reasons set forth in this order, the Court GRANTS
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the joint motion and OVERRULES the objections. The Court DENIES all other pending motions
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as moot.
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SUMMARY
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Plaintiffs Sierra Club and the Natural Resources Defense Council and defendant Regina
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McCarthy, Administrator of the Environmental Protection Agency (“EPA”), have jointly moved
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the Court to approve and enter a proposed consent decree. The proposed consent decree would
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fully resolve plaintiffs’ claims under the Clean Air Act, 42 U.S.C. §§ 7401-7671q, against
defendant based on EPA’s failure to promulgate designations for the 2010 revised primary sulfur
dioxide (“SO2”) national ambient air quality standard. The proposed consent decree sets forth
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mandatory deadlines for EPA to issue designations for all areas of the country that remain
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undesignated.
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The Court finds that the proposed consent decree is procedurally and substantively fair and
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reasonable. A number of states have objected to the proposed consent decree, arguing that where
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the EPA has failed to promulgate air quality designations by the statutory deadline, the Clean Air
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Act requires that the EPA issue “unclassifiable” designations for undesignated areas. As set forth
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in this order, the Court finds that these objections lack merit, and that the Clean Air Act does not
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compel “unclassifiable” designations. In a “deadline suit” such as this, the appropriate remedy is
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to set a binding schedule for the EPA to make all remaining designations, while preserving EPA’s
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discretion to determine, based on available information, whether an area is in “attainment” or
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“nonattainment” with the revised sulfur dioxide air quality standard, or whether the area is
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“unclassifiable.”
The States also object that the proposed consent decree improperly incorporates the EPA’s
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United States District Court
Northern District of California
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proposed Data Requirements Rule for the 1-Hour Sulfur Dioxide (SO2) Primary National Ambient
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Air Quality Standard (NAAQS), 79 Fed. Reg. 27,446 (May 13, 2014).
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Requirements Rule, if adopted, would require state air agencies to provide to EPA data to
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characterize current air quality in areas with large sources of SO2 emissions using either additional
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air quality monitoring or modeling.
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independent of the proposed Data Requirements Rule, and that the deadlines contained in the
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proposed consent decree are not dependent on the Rule’s promulgation.
The proposed Data
The Court finds that the proposed consent decree is
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The Court also finds that the proposed consent decree is procedurally fair. A notice of the
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proposed consent decree was published in the Federal Register on June 2, 2014, and the record
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reflects that 133 public comments were submitted and considered. Prior to the public comment
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process, there were extensive, arms-length negotiations between the parties, with the participation
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of the intervening states, regarding a possible remedy in this case. The intervening states have had
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the opportunity to file objections to the proposed consent decree, and the Court has also permitted
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the filing of several amicus briefs. The Court has carefully considered all of these filings, and the
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record in this case, in reaching the conclusion that the proposed consent decree meets the
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standards for court approval.
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BACKGROUND
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I.
Statutory background
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Pursuant to Title I of the Clean Air Act, the EPA is required to set national ambient air
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quality standards (“NAAQS”) for certain air pollutants. 42 U.S.C. § 7409. A NAAQS sets the
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maximum permissible concentration of the pollutant in the ambient air. Id. Primary NAAQS are
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set at levels “requisite to protect the public health,” with a sufficient margin of safety. Id.
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§ 7409(b)(1). Secondary NAAQS are set at levels “requisite to protect public welfare from any
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known or anticipated adverse effects associated with the presence of such air pollutant in the
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ambient air.” Id. § 7409(b)(2).
Within one year after the EPA establishes or revises a NAAQS, each state is required to
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United States District Court
Northern District of California
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submit to the EPA a list identifying the state’s initial recommended designations for all areas
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within the state. Id. § 7407(d)(1)(A). Pursuant to the Clean Air Act, states may make three types
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of designations: (1) “attainment” for areas that comply with the NAAQS, (2) “nonattainment” for
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areas which do not meet the NAAQS, and (3) “unclassifiable” for “any area that cannot be
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classified on the basis of available information as meeting or not meeting” the NAAQS. Id. EPA
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is required to promulgate designations in response to the states’ recommendations within two
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years after EPA promulgates or revises a NAAQS. Id. § 7407(d)(1)(B). EPA can extend this
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deadline “up to one year in the event the Administrator has insufficient information to promulgate
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the designations.” Id. § 7407(d)(1)(B)(i). In promulgating designations, EPA may make any
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modifications “the Administrator deems necessary” to a state’s recommended designations. Id.
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§ 7407(d)(1)(B)(ii). If EPA modifies a state’s designation, the agency must provide the state with
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a minimum of 120 days notice and an opportunity to show why the agency’s proposed
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modification is incorrect before EPA issues final designations. Id.
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Air quality designations determine what type of federally-required implementation plan is
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appropriate for each area and what permitting standards apply. See, e.g., 42 U.S.C. § 7410
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(general implementation planning requirements), § 7475 (permitting requirements for “attainment”
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and “unclassifiable” areas), § 7503 (permitting requirements for “nonattainment” areas). If an
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area is undesignated, or designated “attainment” or “unclassifiable,” the state is required to
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develop a “state implementation plan” that provides for implementation, maintenance and
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enforcement of the new or revised NAAQS. Id. § 7410(a)(1)-(2). If an area is designated
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“nonattainment,” there are additional planning requirements and stricter new source review
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permitting requirements. Id. §§ 7502-7503, 7514-7514a(b)(1).
On June 2, 2010, EPA revised the primary sulfur dioxide (SO2) air quality standard to
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establish a new 1-hour SO2 NAAQS at a level of 75 parts per billion. “Primary National Ambient
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Air Quality Standard for Sulfur Dioxide; Final Rule,” 75 Fed. Reg. 35,520, 35,525/1-27/3 (June
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22, 2010); 40 C.F.R. § 50.17(a)-(b). In the preamble to that rule, EPA noted that implementation
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of the NAAQS is complicated because of the “unique source specific impacts of SO2 emissions,”
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the complexity of defining the appropriate methods for determining area designations, and the
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United States District Court
Northern District of California
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“potential for substantial SO2 emissions reductions as a result of national and regional rules” that
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were then underway. Id. at 35,550/2-3. EPA also explained that the SO2 monitoring network is
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limited, and that after considering public comments EPA “intend[ed] to use a hybrid analytic
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approach that would combine the use of monitoring and modeling to assess compliance with the
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new 1-hour SO2 NAAQS.” Id. at 35,551. Over the next several years, EPA continued to analyze
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different approaches to implementing the revised NAAQS. See generally Dkt. 95 at 7:16-11:11
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(discussing process); Dkt. 97-3 (“Next Steps for Area Designations and Implementation of the
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Sulfur Dioxide National Ambient Air Quality Standard”) (February 6, 2013).
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Pursuant to Section 107(d)(1)(A) of the Clean Air Act, 42 U.S.C. § 7404(d)(1)(A), the
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states’ recommended designations regarding the revised SO2 NAAQS were due on June 2, 2011.
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The intervening states submitted their designations by the June 2, 2011 deadline. 1 EPA granted
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itself the permitted one-year extension, under which it was required to publish air quality
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designations by June 2, 2013. In granting itself the extension of time to promulgate designations,
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EPA noted the uncertainty as to what “analytic approach sources, states, and EPA will consistently
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and cooperatively use” to make the designations. 77 Fed. Reg. 46,295, 46,297/2-3 (Aug. 3, 2012)
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According to the EPA, “states have been reporting updated monitoring data to EPA since their
recommended designations were submitted in 2011, which in some cases was necessary in order
to obtain a full three-calendar years of monitored data that did not yet exist ‘as of’ June 2013.”
Dkt. 104 at 10:16-19.
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(“Extension of Deadline for Promulgating Designations for the 2010 Primary Sulfur Dioxide
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National Ambient Air Quality Standard”).
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In August 2013, the EPA promulgated “nonattainment” designations for 29 areas in 16
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states where three full calendar years of air quality monitoring data showed violations of the
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standard. “Air Quality Designations for the 2010 Sulfur Dioxide (SO2) Primary National Ambient
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Air Quality Standard,” 78 Fed. Reg. 47,191 (Aug. 5, 2013) (“2013 Designations Rule"). For the
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remaining undesignated areas of the country, the preamble of the 2013 Designations Rule stated:
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In separate future actions, the EPA intends to address the
designations for all other areas for which the agency is not yet
prepared to issue designations and that are consequently not
addressed in this final rule. With input from a diverse group of
stakeholders, EPA has developed a comprehensive implementation
strategy for the future SO2 designations actions that focuses
resources on identifying and addressing unhealthy levels of SO2 in
areas where people are most likely to be exposed to violations of the
standard.
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78 Fed. Reg. at 47,193/3. In response to the 2013 Designations Rule, some commenters criticized
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EPA for its “deferral” of designations. See EPA, Responses to Significant Comments on the State
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and Tribal Designation Recommendations for the 2010 Sulfur Dioxide National Ambient Air
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Quality Standards (NAAQS), at 7 (July 2013), EPA-HQ-OAR-2012-0233-0354 (excerpts
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available at Dkt. 91-5 and Dkt. 154-2). In a section of the EPA's responses titled “Not Yet Taking
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Action on Areas With No Monitored Violation,” EPA stated that it is “not at this time reaching
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any final conclusions about areas that do not have violating monitors” and that “[o]bjections to
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EPA’s not yet addressing other areas are outside the scope of this final action.” Id. at 5, 7. EPA
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also stated that it “is not yet taking any final action regarding other areas,” and that “[i]t is
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therefore not necessary for EPA to respond to the points raised by these comments regarding other
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areas that are not addressed in this initial action.” Id. at 5.
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United States District Court
Northern District of California
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In a separate but related regulatory action, in May 2014 EPA published a proposed Data
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Requirements Rule which, if promulgated, would direct state air agencies to characterize air
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quality in those locations defined in the rule as priority areas using the state agency’s choice of
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either additional air quality monitoring or modeling, and to submit such data to EPA to support
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further designations. See Data Requirements Rule for the 1-Hour Sulfur Dioxide (SO2) Primary
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National Ambient Air Quality Standard (NAAQS), 79 Fed. Reg. 27,446 (May 13, 2014). A final
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Data Requirements Rule has not yet been promulgated.
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II.
This litigation and proposed consent decree
On August 26, 2013, plaintiffs Sierra Club and the Natural Resources Defense Council
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filed this complaint under the citizen suit provision of the Clean Air Act, 42 U.S.C. § 7604(a)(2),
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seeking to compel defendant to perform her non-discretionary duty under the Clean Air Act to
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promulgate and publish designations identifying all areas of the nation that meet or fail to meet the
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revised SO2 NAAQS, as well as all areas of the nation where information is inadequate to make a
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designation. On October 3, 2013, Sierra Club also filed a protective petition for review of the
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United States District Court
Northern District of California
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2013 Designations Rule. See Sierra Club v. EPA, D.C. Cir. Case No. 13-1262, Doc. #1515525
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(Environmental Petitioners’ Motion to Deconsolidate Case No. 13-1262 and Hold It in Abeyance).
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Dkt. 154, Ex. A at 5-6 (Sierra Club Motion to Deconsolidate Petition, describing protective
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filing). In the petition for review, Sierra Club stated the issue presented as “whether EPA acted
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illegally and arbitrarily by failing to include sulfur dioxide designations for all areas of the country
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in the final action at issue here.” Id. at 6. That petition has been stayed. Dkt. 161 at 10:3-9.
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In this action, plaintiffs moved for summary judgment on liability, which defendant did not
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dispute. In an order filed December 6, 2013, the Court found as a matter of law that defendant "is
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in violation of her non-discretionary duty under the Clean Air Act, 42 U.S.C. § 7407(d)(1)(B),
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(d)(2)(A) to promulgate and publish designations for all areas of each state for the standard no
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later than three years from promulgation of the standard." Dkt. 79 at 3:18-20. In the same order,
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the Court granted two motions for permissive intervention filed by the Commonwealth of
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Kentucky Energy and Environment Cabinet, the State of Louisiana Department of Environmental
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Quality, and the states of North Carolina, North Dakota, Arizona, Nevada and Texas (collectively
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“the States”). On January 15, 2014, North Carolina filed a complaint in intervention to “compel
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the Administrator of the U.S. Environmental Protection Agency (‘Administrator’ or ‘EPA’), to
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take action mandated by the Clean Air Act, 42 U.S.C. § 7401 et seq. (‘CAA’) to designate areas
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within North Carolina as nonattainment or attainment/unclassifiable for the revised National
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Ambient Air Quality Standard ('NAAQS') for sulfur dioxide (SO2).” Intervenor Compl. ¶ 1, Dkt.
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83. As with plaintiffs’ complaint in this case, North Carolina’s complaint was filed pursuant to
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the Clean Air Act's citizen suit provision, 42 U.S.C. § 7604(a). The other intervenor states did not
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file a complaint in intervention.
The Court directed the parties and intervenor states to meet and confer regarding a possible
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remedy. The parties and the States engaged in settlement discussions, including at least ten group
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settlement conference calls and exchanges of settlement proposals. Dkt. 121-1 ¶¶ 6-8. EPA also
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had separate settlement discussions with certain of the states and with the plaintiffs. Id. ¶¶ 10-11.
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The general approach adopted in the proposed consent decree, which requires EPA to complete
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designations in three phases, was proposed and discussed in the group settlement negotiations. Id.
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United States District Court
Northern District of California
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¶ 8. After the parties reached an impasse in their negotiations, they filed extensive briefing on
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competing proposals for a remedy. During the briefing process, EPA and plaintiffs reached a
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tentative settlement agreement, and on May 19, 2014, EPA and plaintiffs lodged the proposed
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consent decree with the Court. The Court then granted EPA’s motion to stay these proceedings
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until August 1, 2014, pending the public comment process regarding the proposed consent decree.
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A notice of the proposed consent decree was published in the Federal Register on June 2, 2014,
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seeking comment on the proposed decree. 79 Fed. Reg. at 31,325. One hundred and thirty three
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public comments were filed, including many by the intervenor states and amici in this case.
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On August 8, 2014, the parties filed a joint motion to approve and enter the proposed
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consent decree.
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opposition brief was filed collectively by the Commonwealth of Kentucky, Energy and
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Environment Cabinet, the Louisiana Department of Environmental Quality, and the states of
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Arizona, Nevada, North Dakota, and Texas. Dkt. 127. The Court also permitted amicus filings by
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the states of Nebraska, Alabama, Alaska, Arkansas, Georgia, Indiana, Kansas, Louisiana, Ohio,
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Oklahoma, South Carolina, South Dakota, West Virginia, and Wyoming, as well as the National
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Environmental Development Association’s Clean Air Project (“NEDA/CAP”) and the Texas SO2
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Working Group. Dkt. 135, 148.
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Dkt. 124.
North Carolina filed a brief opposing approval, and a separate
The proposed consent decree would require EPA to issue all remaining designations
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according to a three-phase schedule that applies nationwide. Proposed Consent Decree at ¶¶ 1-3,
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Dkt. 120-2. First, within 16 months of the entry of the consent decree, EPA would sign for
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publication designations for those areas that, based on air quality monitoring in the preceding three
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full calendar years, have monitored violations of the revised SO2 standard. Id. ¶ 1(a). By the
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same date, EPA would issue designations for areas that “contain any stationary source that has not
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been ‘announced for retirement’ . . . and that, according to the data in EPA’s Air Markets
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Database, either (1) emitted more than 16,000 tons of SO2 in 2012, or (2) emitted more than 2,600
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tons of SO2 and had an annual average emission rate of at least 0.45 lbs SO2/Mmbtu or higher in
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2012.” Id. ¶ 1(b)-(c). EPA states that “the areas that fall within paragraph 1(b) contain the largest
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sources of SO2 emissions in the country and may have SO2 levels that cause areas to exceed the
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United States District Court
Northern District of California
1
standard.” Dkt. 121 at 8:1-2.
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Second, by December 31, 2017, EPA would sign for publication designations “for
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remaining undesignated areas in which, by January 1, 2017, states have not installed and begun
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operating a new SO2 monitoring network meeting EPA specifications referenced in EPA’s
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anticipated rulemaking [the Data Requirements Rule] directing states to collect and analyze
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additional information regarding SO2 emissions concentrations.” Id. ¶ 2. In the final round, by
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December 31, 2020, EPA would sign for publication designations for all remaining undesignated
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areas. Id. ¶ 3. The proposed decree provides that it does not “limit or modify the discretion
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accorded EPA by the CAA and by general principles of administrative law, including the
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discretion to alter, amend or revise any response and/or final action contemplated by [the proposed
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consent decree].” Id. ¶ 7. The proposed consent decree would establish binding deadlines even if
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the Data Requirements Rule is not adopted. However, if the Data Requirements Rule is adopted,
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the data collection process proposed in the rule could be used to support EPA’s designations under
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the consent decree.
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LEGAL STANDARD
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Approval of a proposed consent decree is within the discretion of the Court. United States
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v. Oregon, 913 F.2d 576, 580 (9th Cir. 1990). A court reviews a consent decree to determine
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whether it is “fundamentally fair, adequate and reasonable.” Id. The Court must evaluate both the
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procedural and substantive fairness of the consent decree. United States v. Chevron, 380 F. Supp.
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2d 1104, 1110-11 (N.D. Cal. 2004). In addition, while a consent decree “must conform to
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applicable laws . . . [it] need not impose all the obligations authorized by law.” United States v.
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Oregon, 913 F.3d at 580.
The Court’s review of the proposed consent decree is informed by the public policy
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favoring settlement. See United States v. Comunidades Unidas Contra La Contaminacion, 204
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F.3d 275, 280 (1st Cir. 2000). “This deference is particularly strong where the decree has been
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negotiated by the Department of Justice on behalf of an agency like the EPA which is an expert in
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its field.” Chevron, 380 F. Supp. 3d at 1111. However, when reviewing a proposed consent
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United States District Court
Northern District of California
6
decree, the Court must independently evaluate its terms and avoid giving a “rubber stamp
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approval.” United States v. Montrose Chem. Corp. of Cal., 50 F.3d 741, 747 (9th Cir. 1995)
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(quoting City of Detroit v. Grinnell Corp., 495 F.2d 448, 462 (2d Cir. 1974)).
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In applying the “fair, adequate and reasonable” standard, courts examine both procedural
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and substantive fairness. See United States v. Cannons Engineering Corp., 899 F.2d 79, 86 (1st
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Cir.1990). With regard to procedural fairness, courts determine whether the negotiation process
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was “fair and full of adversarial vigor.” United States v. Telluride Co., 849 F. Supp. 1400, 1402
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(D. Colo. 1994) (citations and internal quotations omitted). If the decree was the product of “good
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faith, arms-length negotiations,” it is “presumptively valid and the objecting party has a heavy
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burden of demonstrating the decree is unreasonable.” United States v. Oregon, 913 F.2d at 581.
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However, “the district court must ensure that the agreement is not . . . a product of collusion . . .”).
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United States v. Colorado, 937 F.2d 505, 509 (10th Cir.1991)
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With respect to substantive fairness, it is not the duty of the court to determine whether
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“the settlement is one which the court itself might have fashioned, or considers ideal.” Cannons,
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899 F.2d at 84; see also BP Exploration, 167 F. Supp. 2d at 1050 (stating that court should refrain
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from “substitut[ing] its judgment for that of the parties”). Instead, the “court’s approval is nothing
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more than an amalgam of delicate balancing, gross approximations and rough justice.” Oregon,
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913 F.2d at 581 (internal quotations omitted). “The court need only be satisfied that the decree
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represents a reasonable factual and legal determination.” Id. (internal quotation omitted).
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DISCUSSION
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I.
Jurisdiction
Plaintiffs filed this action pursuant to the Clean Air Act’s citizen suit provision, 42 U.S.C.
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§ 7604(a)(2). That provision authorizes “any person” to commence a civil action in district court
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“against the Administrator where there is an alleged failure of the Administrator to perform any
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act or duty under this chapter which is not discretionary with the Administrator.” Id. The parties
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and the intervenor states assert that this Court has jurisdiction over this lawsuit pursuant to the
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citizen suit provision because plaintiffs seek to compel the Administrator to perform her non-
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United States District Court
Northern District of California
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discretionary duty to issue designations for the remaining areas in the country.
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On September 12, 2014, non-parties Texas SO2 Working Group and NEDA/CAP sought
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leave, which the Court granted, to file an amicus brief arguing that this Court lacks jurisdiction
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over this action. Amici contend that the EPA’s 2013 Designations Rule includes EPA’s “decision
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to defer” the remaining area designations for the revised SO2 NAAQS, and that this decision is a
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final agency action that may only be challenged in the Court of Appeals for the District of
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Columbia Circuit pursuant to the Clean Air Act’s judicial review provision, 42 U.S.C. § 7607(b).
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That provision states, inter alia, that challenges to any “nationally applicable regulations
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promulgated, or final action taken, by the Administrator under [the Clean Air Act] may be filed
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only in the United States Court of Appeals for the District of Columbia.” Id. § 7607(b)(1). In
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addition, “[w]here a final decision by the Administrator defers performance of any
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nondiscretionary statutory action to a later time, any person may challenge the deferral pursuant to
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[7607(b)(1)].” Id. § 7607(b)(2). Under the Clean Air Act, jurisdiction for review of final agency
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actions and jurisdiction to compel nondiscretionary agency action are mutually exclusive. Envtl.
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Def. Fund v. Costle, 448 F. Supp. 89, 92-93 (D.D.C. 1978).
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The Clean Air Act provides for jurisdiction in the circuit courts of appeal only for “‘final”
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agency actions. Portland Cement Ass’n v. EPA, 665 F.3d 177, 193 (D.C. Cir. 2011). In order to
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be a “final agency action,” the action must meet two conditions. Bennett v. Spear, 520 U.S. 154,
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177-78 (1997). First, the action must “mark the ‘consummation’ of the agency’s decisionmaking
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process—it must not be of a merely tentative or interlocutory nature.” Id. Second, “the action
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must be one by which ‘rights or obligations have been determined,’ or from which ‘legal
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consequences will flow.’” Id. at 178 (citations omitted). Amici argue that this case is similar to
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Maine v. Thomas, 874 F.2d 883 (1st Cir. 1989), in which the First Circuit held that an EPA
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rulemaking stating that the agency would engage in further agency action to promulgate
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regulations amounted to a “final action taken,” and thus that the district court lacked jurisdiction
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over a citizen suit to compel EPA to issue the regulations. Id. at 891. At issue was EPA’s decision
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to defer promulgating regional haze regulations pursuant to § 169 of the Clean Air Act, 42 U.S.C.
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United States District Court
Northern District of California
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§ 7491. Id. at 885-86. The EPA stated in the preamble to the regional haze rulemaking that:
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Future phases will extend the visibility program by addressing more
complex problems such as regional haze and urban plumes. We will
propose and promulgate future phases when improvement in
monitoring techniques provides more data on source-specific levels
of visibility impairment, regional scale models become refined, and
our scientific knowledge about the relationships between emitted air
pollutants and visibility impairment improves.
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45 Fed. Reg. 80,084, 80,086 (Dec. 2, 1980). The First Circuit held that the rulemaking, referred to
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as “Phase 1,” was a final agency action because,
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EPA announced Phase 1 as a regulatory scheme, fully explained and
defended in the text setting out the regulations. Furthermore, the
administrative proceedings had directly addressed the possibility
that regional haze rules and orders might be delayed. To mince no
words, the decision to defer constituted a fully developed part of the
final action taken on the statutory mandate. . . . [T]he final action
taken has legal effect and establishes procedural requirements, such
as substantive conditions and consequent deadlines, for establishing
future phases.
Maine, 874 F.2d at 887-88.
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The parties respond that EPA’s 2013 Designations Rule is a final agency action only with
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respect to the 29 areas that were designated in that rule. The parties contend that the statement in
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the preamble that "[i]n separate future actions, the EPA intends to address the designations for all
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other areas for which the agency is not yet prepared to issue designations and that are
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consequently not addressed in this final rule," 78 Fed. Reg. at 47,193/3, does not reflect the
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culmination of any decisionmaking process with respect to the undesignated areas, and simply
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recognized that the 2013 Designations Rule did not include designations for all areas of the
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country and that EPA’s designations process would continue. 78 Fed. Reg. 47,197-205 (setting
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forth the revisions to 40 C.F.R. Part 81, Subpart C). The parties argue that, unlike Maine v.
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Thomas, where “the decision to defer constituted a fully developed part of the final action taken on
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the statutory mandate,” here the 2013 Designations Rule did not contain any analysis of the states’
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recommendations regarding the undesignated areas, nor did EPA address the available information
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concerning emissions levels in those areas. The parties argue that the 2013 Designations Rule did
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not include any proposals regarding intended future designations for areas outside the scope of the
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2013 Designations Rule, nor did it contain a schedule for future action.
The parties contend that this case is more similar to Portland Cement Association v. EPA,
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United States District Court
Northern District of California
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665 F.3d 177 (D.C. Cir. 2011) (per curiam). In Portland Cement, environmental groups filed a
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petition for review in the D.C. Circuit challenging EPA’s failure to regulate greenhouse gasses
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from cement facilities as part of a rule establishing emissions standards for such facilities under
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the Clean Air Act. Id. at 182. In the preamble to the challenged rule, EPA stated that it did “not
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yet have adequate information about greenhouse gas emissions to set a standard,” and that it was
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“working towards a proposal for greenhouse gas standards,” which it would issue after obtaining
17
additional information. Id. at 184. The D.C. Circuit held that these “explicitly tentative and
18
conditional statements—which expressed certainty only as to EPA’s decision to continue the
19
process of studying greenhouse gases” could not “possibly be considered ‘final.’” Id. at 193.
20
The Court concludes that the preamble statement in the 2013 Designations Rule is not a
21
final agency action, and thus that this Court has jurisdiction over this case. As an initial matter,
22
the Court notes that "[w]hile preamble statements may in some unique cases constitute binding,
23
final agency action susceptible to judicial review, this is not the norm." Natural Res. Def. Council
24
v. EPA, 559 F.3d 561, 564-65 (D.C. Cir. 2009) (internal citation omitted); see also American
25
Petroleum Institute v. E.P.A., 684 F.3d 1342, 1354 (D.C. Cir. 2012) (holding preamble statement
26
that permit applicants "will initially be required" to meet certain standards "could reasonably be
27
read to mean the EPA intends in the future to establish such a requirement, in which case the
28
statement falls short of being the consummation of the agency's decisionmaking process.").
12
Here, the preamble statement does not represent the consummation of any agency
2
decisionmaking or alter the status quo. Unlike in Maine, where "the decision to defer constituted a
3
fully developed part of the final action taken on the statutory mandate," the administrative record
4
for the 2013 Designations Rule does not contain any analysis for the undesignated areas, nor does
5
it contain an analysis of the decision to defer promulgating designations. See generally 78 Fed.
6
Reg. 47,191; Docket ID No. EPA-HQ-OAR-2012-0233 at www.regulations.gov.
7
administrative record shows that in responding to public comments submitted in connection with
8
EPA's notice of proposed designations, EPA repeatedly stated that it was "not yet taking any final
9
action regarding other areas [aside from the 29 areas designated as "nonattainment"] . . . and EPA
10
has neither proposed action for those areas nor taken final action for them in this round of
11
United States District Court
Northern District of California
1
designations." Dkt. 154-2 at 5 (Responses to Significant Comments on the State and Tribal
12
Designation Recommendations for the 2010 Sulfur Dioxide National Ambient Air Quality
13
Standards (NAAQS), at 7 (July 2013), EPA-HQ-OAR-2012-0233-0354). Like the “explicitly
14
tentative and conditional statements” in Portland Cement “which expressed certainty only as to
15
EPA’s decision to continue the process of studying greenhouse gases,” EPA’s statement in the
16
preamble to the 2013 rule was simply an indication that EPA was “not yet prepared to address” the
17
undesignated areas, and that EPA will “continue to work” with stakeholders to obtain the data to
18
assist in preparing those designations. 78 Fed. Reg. at 47,191/3, 47,193/3-94/1. Both the language
19
of the preamble statement and the context of the entire 2013 Designations Rule demonstrate that
20
the preamble statement is of an interlocutory nature, and not a “consummation of the agency’s
21
decisionmaking process.” American Petroleum Institute, 684 F.3d at 1354 ("By acknowledging it
22
had not yet, but 'w[ould] need to[,] ... carefully evaluate[ ]' the effect of the new NAAQS on the
23
permitting process, the EPA made clear it was not making a final decision."); cf. Nat’l Ass’n of
24
Home Builders v. Norton, 415 F.3d 8, 14 (D.C. Cir. 2005) (“An agency’s past characterization of
25
its own action, while not decisive, is entitled to respect in a finality analysis.”).
The
26
27
28
II.
Approval of the consent decree
The intervenor and amici states raise a number of objections to the proposed consent
13
1
decree, and they contend that the proposed consent decree lacks substantive and procedural
2
fairness. For the reasons set forth below, the Court concludes that the proposed consent decree is
3
fair and reasonable, both procedurally and substantively, and consistent with the Clean Air Act
4
and other applicable law.
The central dispute between the parties and the intervenor and amici states is whether
6
EPA’s failure to promulgate area designations by the statutory deadline requires EPA to
7
promulgate “unclassifiable” designations for all undesignated areas, or whether EPA may, as set
8
forth in the proposed consent decree, have additional time to complete the designation process and
9
issue “attainment,” “nonattainment,” or “unclassifiable” designations based upon the data before
10
the agency. The States argue the proposed consent decree violates Section 107(d)(1)(B), which
11
United States District Court
Northern District of California
5
provides,
12
15
Upon promulgation or revision of a national ambient air quality
standard, the Administrator shall promulgate the designations of all
areas . . . as expeditiously as practicable, but in no case later than 2
years from the date of promulgation of the new or revised national
ambient air quality standard. Such period may be extended for up to
one year in the event the Administrator has insufficient information
to promulgate the designations.
16
42 U.S.C. § 7407(b)(ii). The States argue that the statute allows EPA no more than three years
17
from the date it finalizes a new NAAQS to complete the area designation process, and that the
18
proposed consent decree improperly allows EPA additional time to complete that process. The
19
States argue that “EPA does not have to designate the remaining areas ‘unclassifiable’ because it
20
missed the deadline. EPA must designate the areas ‘unclassifiable’ because it lacks the data it
21
needs to make any other designation.” Dkt. 135 at 6:13-16.
13
14
22
North Carolina cites Sierra Club v. E.P.A., 762 F.3d 971 (9th Cir. 2014), for the
23
proposition that when EPA misses a deadline, the “same standards apply both before and after the
24
deadline and EPA does not ‘possess[] the power’ now that it has missed the deadline, ‘to resolve
25
the matter as it sees fit.’” Dkt. 124 at 8:7-9 (quoting Sierra Club, 762 F.3d at 981). In Sierra
26
Club, Avenal Power Center applied to the EPA for a permit to build and operate a power plant.
27
Although the Clean Air Act imposed a duty on EPA to either grant or deny the permit application
28
within one year, EPA failed to do so. After the deadline passed but before EPA took final action
14
on the permit application, EPA promulgated more stringent air quality standards. Avenal sued
2
EPA, seeking to compel EPA to issue the permit under the old standards that would have applied
3
if EPA had issued the permit by the statutory deadline. After initially stating that the Clean Air
4
Act required EPA to apply the regulations in effect at the time of the permitting decision, EPA
5
changed course and granted the permit under the old standards, asserting that it had
6
“grandfathering authority.” The Sierra Club brought suit challenging EPA’s action, and the Ninth
7
Circuit held "[t]he plain language of the statute . . . clearly requires EPA to apply the regulations in
8
effect at the time of the permitting decision." Id. at 979. The sections of the Clean Air Act
9
interpreted in Sierra Club are different from those at issue in this case. However, relevant here, in
10
rejecting the EPA's contention that it had the authority to issue the permit under the old standards,
11
United States District Court
Northern District of California
1
the Ninth Circuit stated,
12
13
14
15
16
17
18
19
20
21
22
23
Nothing in the statute precludes EPA from enforcing current
NAAQS and BACT requirements even if it unreasonably delays
taking action on a Permit. Moreover, the Clean Air Act is not silent
about the consequences of such delay. “Congress has directly
spoken to [that] precise issue”—namely, by providing a private right
of action to compel timely action. Chevron [U.S.A., Inc. v. Natural
Resources Defense Council, Inc., 467 U.S. 837, 842 (1984)]. Under
42 U.S.C. § 7604(a)(2):
Except as provided in subsection (b) of this section,
any person may commence a civil action on his own
behalf . . . against the Administrator where there is
alleged a failure of the Administrator to perform
any act or duty under this chapter which is not
discretionary with the Administrator.
Avenal Power, of course, availed itself of this remedy and brought
suit in the D.C. district court. That court, correctly in our view, did
not find the appropriate remedy to be issuance of the Permit without
regard to the newly-promulgated regulations. Instead, it simply
ordered the agency to come to a final decision. See Avenal Power
Ctr., LLC v. EPA, 787 F.Supp.2d 1, 4–5 (D.D.C. 2011).
Id. at 980-81 (internal footnote omitted). The Ninth Circuit also noted,
24
25
26
27
28
We find Brock v. Pierce Cnty., 476 U.S. 253, 256, 106 S.Ct. 1834,
90 L.Ed.2d 248 (1986), instructive in this regard. In Brock, a sincerepealed provision of the Comprehensive Employment and Training
Act required the Secretary of Labor to issue a final determination as
to the misuse of certain funds within 120 days after receipt of a
complaint alleging misuse. Id. Although the statute used mandatory
language requiring the Secretary to investigate and issue formal
findings, it did not specify consequences for the Secretary's failure
15
to act. Id. at 258–59, 106 S.Ct. 1834. The Court rejected the
argument that the 120–day period was a statute of limitations that
barred the Secretary from taking further action on the complaint
after the 120–day period expired, reasoning: “We would be most
reluctant to conclude that every failure of an agency to observe a
procedural requirement voids subsequent agency action, especially
when important public rights are at stake.” Id. at 260, 106 S.Ct.
1834. And the Court then concluded, instead: “When, as here, there
are less drastic remedies available for failure to meet a statutory
deadline, courts should not assume that Congress intended the
agency to lose its power to act.” Id. (footnote omitted). The
appropriate relief, the Court noted, was an order compelling the
agency to act. Id. at 260 n. 7, 106 S.Ct. 1834.
1
2
3
4
5
6
7
Id. at 981 n.5. Thus, rather than supporting the States' position, Sierra Club holds that the
8
appropriate relief in a deadline suit is to compel the agency to act, rather than ordering a particular
9
substantive outcome. See also Kennecott Copper Corp. Nev. Mines Div., McGill Nev. v. Costle,
10
572 F.2d 1349, 1354 (9th Cir. 1978) (holding EPA had non-discretionary duty to make a decision
United States District Court
Northern District of California
11
12
about state’s revision of its CAA state implementation plan, but that EPA “retains a good deal of
discretion as to the content of that decision”); Frey v. EPA, 751 F.3d 461, 469 (7th Cir. 2014)
13
("Our review of the EPA's actions is limited. . . . to allow review only of whether the EPA
14
followed required decision-making procedures. . . . The substance of the EPA's decisions, on the
15
other hand, is at least partly discretionary, and therefore beyond the scope of these citizen suit
16
provisions.").
17
North Carolina also asserts that the proposed consent decree would allow EPA to avoid
18
having to make "unclassifiable" designations. However, the proposed consent decree preserves
19
EPA's discretion to make designations of "nonattainment," "attainment," or "unclassifiable" based
20
upon the information before the EPA, and nothing in the proposed consent decree precludes EPA
21
from ultimately issuing "unclassifiable" designations.
22
The States of Nebraska et al., cite an EPA brief in Mississippi Commission on
23
Environmental Quality v. EPA, Case. No. 12-1309 (and consolidated cases), 2013 WL 6529643
24
(filed Mar. 20, 2014), and Catawba County, N.C. v. EPA, 571 F.3d 20, 26 (D.C. Cir. 2009), to
25
argue that the Clean Air Act "requires an unclassifiable designation when the available
26
information does not permit a finding of attainment or nonattainment." Dkt. 135 at 6:20-7:2. At
27
issue in those cases was whether specific air-quality designations were flawed or not supported by
28
16
1
data. Neither case stands for the proposition that the EPA must issue "unclassifiable" designations
2
in circumstances where, as is the situation here, EPA has repeatedly explained that there was
3
uncertainty as to how to best characterize SO2 emissions for purposes of implementing the revised
4
SO2 standard, and EPA was working with the states, tribes, and other entities to address that issue
5
before reviewing the information before the EPA. Contrary to the states' arguments, the EPA has
6
not stated that it lacks sufficient information to issue designations for the remaining areas, but
7
rather that because of the uncertainty regarding how to best characterize emissions, it was "not yet
8
prepared to issue designations." 78 Fed. Reg. 47,191.
Here, although Section 107(d)(1)(B) uses mandatory language requiring EPA to
10
promulgate air-quality designations no later than two years from the date of promulgation of the
11
United States District Court
Northern District of California
9
new or revised national ambient air quality standard, the Clean Air Act does not specify what
12
happens in the event that EPA misses a designation deadline. The Court finds it significant that
13
Congress did not prescribe a default consequence for violation of the deadline, as it did in other
14
places in the Clean Air Act.
15
nonattainment by operation of law for particular areas); § 7410(k)(1)(B) (stating that if EPA fails
16
to make a determination that a state implementation plan fails to meet minimum criteria by the
17
statutory deadline, the plan is deemed by operation of law to meet such criteria);
18
§ 7545(o)(2)(A)(i), (iv) (requiring that EPA promulgate renewable fuel regulations by August 8,
19
2006, but providing that “[i]f the Administrator does not promulgate regulations under clause (i),
20
the percentage of renewable fuel in gasoline . . . shall be 2.78 percent for calendar year 2006”).
21
Under Sierra Club and Brock, the appropriate remedy in a “deadline” case such as this is to
22
require EPA to issue designations pursuant to a schedule, not to mandate that EPA issue any
23
particular designation.
See 42 U.S.C. §§ 7407(d)(1)(C) (discussing designations of
24
The States also contend that the proposed consent decree does far more than set a binding
25
and enforceable schedule for EPA to complete remaining designations, and that it establishes
26
duties and obligations beyond EPA’s authority. The States assert that paragraph 1(b) of the
27
proposed consent decree intrudes on EPA’s discretion in making designations, such that
28
“designations can be based on the mere presence of very specific and large emitting sources of
17
1
SO2 in a certain area.” Dkt. 127 at 11:25-12:6. However, paragraph 1(b) does not affect EPA’s
2
discretion to determine the particular designation for an area, and instead only provides that
3
certain areas containing large sources of SO2 pollution are required to be designated by EPA
4
within 16 months of entry of the decree.
The States also assert that the proposed consent decree “discard[s]” the “work that the
5
6
Intervenor States completed to make their initial designations” or “may” render the work “stale.”
7
Dkt. 124 at 18-19; Dkt. 127 at 15:3-5. However, the States do not cite any language in the
8
proposed consent decree that renders invalid or obsolete the earlier information provided by the
9
States.
The parties state that the initial recommendations and accompanying information
submitted by the states remain in the administrative record for consideration by EPA. See Dkt.
11
United States District Court
Northern District of California
10
132 at 6:4-6. Further, in making designations pursuant to the decree, EPA must comply with the
12
statutory procedure for promulgating designations based on state recommendations, which
13
includes notifying states of any intended modifications to their recommendations no later than 120
14
days before the date of promulgation and allowing them an opportunity to demonstrate why any
15
designation is inappropriate. See 42 U.S.C. § 7404(d)(1)B)(ii).
16
The intervenor States also argue that the proposed consent decree improperly deprives
17
them of their claims. However, to the extent that the States are concerned about the effect of this
18
litigation on other pending cases, the parties state that "[a]ny decision by this Court to enter the
19
proposed consent decree would not, in and of itself, result in the dismissal of the Plaintiff-
20
Intervenors' claims in those suits. That is, if the Court enters the proposed consent decree here,
21
those parties will still be free to pursue earlier deadlines in those actions (with respect to remaining
22
undesignated areas within their states)." Dkt. 132 at 12:16-20. With respect to the intervenors'
23
claims in this case, only North Carolina has filed a complaint in intervention, and that complaint
24
requests that the Court "[i]ssue a mandatory injunction requiring the Administrator to perform her
25
mandatory duties by a certain date set by the Court." Dkt. 83 at 6. Thus, rather than depriving
26
North Carolina of its claims, the proposed consent decree provides North Carolina with the relief
27
sought, namely a binding schedule to issue all remaining designations.
28
The remainder of the States' substantive objections relate to the proposed Data
18
Requirements Rule. The States assert that paragraphs 2 and 3 of the proposed consent decree
2
“dictate the mechanism that States must use in collecting new data for EPA.” Dkt. 127 at 11:15-
3
17. However, those paragraphs only set a deadline for issuing designations for those areas in
4
which, by January 1, 2017, states have not installed and begun operating a new SO2 monitoring
5
network, and a later deadline for all remaining undesignated areas. Similarly, although the States
6
may need to supplement and update their previous submissions if the Data Requirements Rule is
7
adopted, that would be a consequence of the Data Requirements Rule, not the proposed consent
8
decree. The States also complain that the proposed consent decree "violates the Administrative
9
Procedure Act ('APA') and undermines the [Data Requirements Rule] rule-making process." Dkt.
10
135 at 8:15-16. However, the States do not explain how the proposed consent decree violates the
11
United States District Court
Northern District of California
1
APA, 5 U.S.C. § 553, which applies to agency "rule making," and does not apply to promulgation
12
of air quality designations. See 5 U.S.C. § 551(4-)(5)(defining "rule making" and "rule"); 42
13
U.S.C. § 7407(d)(2)(B) ("Promulgation or announcement of a designation under paragraph (1) . . .
14
Shall not be subject to the provisions of sections 553 through 557 of Title 5 (relating to notice and
15
comment)."). The Court also finds that the proposed consent decree does not undermine the
16
separate Data Requirements Rule process, as the proposed consent decree is independent of the
17
Data Requirements Rule process. The proposed consent decree was subject to public comment,
18
and the Data Requirements Rule has been subject to its own separate public rule-making process.
19
Finally, the States assert that the proposed consent decree was procedurally unfair because
20
a number of the amici states did not participate in settlement negotiations, and the EPA and
21
plaintiffs had settlement negotiations that did not involve the intervenor States. North Carolina
22
also asserts that the settlement is collusive.
23
The Court finds that these objections lack merit. With regard to the amici states, with the
24
exception of the State of Louisiana (which is also an intervenor), it is undisputed that none of the
25
amici States sought to become parties to this action. The amici States do not cite any authority for
26
the proposition that they should have been invited to participate in settlement discussions in order
27
to assure procedural fairness. The Court also notes that the State of Louisiana, through the
28
Counsel for the Louisiana Department of Environmental Quality, participated in the discussions
19
1
held by the parties between mid-December 2013 and mid-May 2014. See Dkt. 121-1 at ¶¶ 4-8.
The record shows that the proposed consent decree is result of adversarial negotiations
3
conducted over approximately six months, during which the seven state intervenors participated in
4
at least ten settlement calls with the parties. Dkt. 121-1 ¶¶ 6-8. Although the intervenor states
5
complain that EPA and plaintiffs had separate negotiations that resulted in the proposed consent
6
decree, that fact does not mean that the proposed consent decree lacks procedural fairness. The
7
intervenor states also had separate negotiations with EPA that did not include plaintiffs. Id. ¶¶ 10-
8
11. Further, the approach taken in the proposed consent decree was discussed in the group
9
settlement negotiations that included the intervenor states. Id. ¶ 8. Importantly, the proposed
10
consent decree was subject to public comment, and both the amici and intervenor states
11
United States District Court
Northern District of California
2
participated in that process. 78, Fed. Reg. at 31,325; Dkt. 126-2. Finally, there is no support
12
whatsoever for North Carolina's assertion that the proposed consent decree is "a collusive attempt"
13
to secure an illegal remedy.
14
CONCLUSION
15
16
For the reasons set forth above, the Court concludes that the proposed consent decree is
17
fair and reasonable, both procedurally and substantively, and consistent with the Clean Air Act,
18
and other applicable law. Accordingly, the Court GRANTS the parties' joint motion to approve
19
and enter the proposed consent decree.
20
21
IT IS SO ORDERED.
22
23
24
25
Dated: March 2, 2015
______________________________________
SUSAN ILLSTON
United States District Judge
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