Alaska Dept. of Environmental Conservation v. Epa, No. 02-658.

Citation540 U.S. 461
Decision Date21 January 2004
Docket NumberNo. 02-658.
PartiesALASKA DEPARTMENT OF ENVIRONMENTAL CONSERVATION <I>v.</I> ENVIRONMENTAL PROTECTION AGENCY ET AL.
CourtUnited States Supreme Court

The Clean Air Act's (CAA or Act) Prevention of Significant Deterioration (PSD) program, 42 U.S.C. § 7477, was designed to ensure that the air quality in "attainment areas," i.e., areas that are already "clean," will not degrade, see § 7470(1). The program bars construction of any major air pollutant emitting facility not equipped with "the best available control technology" (BACT). § 7475(a)(4). The Act defines BACT as "an emission limitation based on the maximum degree of [pollutant] reduction... which the [state] permitting authority, on a case-by-case basis, taking into account energy, environmental, and economic impacts and other costs, determines is achievable for [the] facility." § 7479(3). Two provisions of the Act vest enforcement authority in the Environmental Protection Agency (EPA or Agency). Section 113(a)(5) generally authorizes the EPA, when it finds that a State is not complying with a CAA "requirement" governing construction of a pollutant source, to pursue remedial action, including issuance of "an order prohibiting the construction." 42 U.S.C. § 7413(a). Directed specifically to the PSD program, CAA § 167 instructs EPA to "take such measures, including issuance of an order.... as necessary to prevent the construction" of a major pollutant emitting facility that does not conform to the "requirements" of the program. Because EPA has classified northwest Alaska, the region here at issue, as an attainment area for nitrogen dioxide, the PSD program applies to emissions of that pollutant in the region. No "major emitting facility," including any source emitting more than 250 tons of nitrogen oxides per year, § 7479(1), may be constructed or modified unless a PSD permit has been issued for the facility, § 7475(a)(1). A PSD permit may not issue unless the proposed facility is subject to BACT for each CAA-regulated pollutant emitted from the facility. § 7475(a)(4).

In this case, "the permitting authority" under § 7479(3) is Alaska, acting through petitioner, the Alaska Department of Environmental Conservation (ADEC). In 1988, Teck Cominco Alaska, Inc. (Cominco), obtained authorization to operate a zinc concentrate mine in northwest Alaska. The mine is a "major emitting facility" under § 7475. Its initial PSD permit authorized five diesel electric generators, MG-1 through MG-5, subject to operating restrictions. Under a second PSD permit issued in 1994, Cominco added a sixth generator, MG-6. In 1996, Cominco initiated a project to expand zinc production by 40% and applied to ADEC for a PSD permit to allow, inter alia, increased electricity generation by MG-5. ADEC preliminarily proposed as BACT for MG-5 an emission control technology known as selective catalytic reduction (SCR), which reduces nitrogen oxide emissions by 90%. Amending its application, Cominco added a seventh generator, MG-17, and proposed, as BACT, an alternative control technology — Low NOx — that achieves a 30% reduction in nitrogen oxide pollutants. In May 1999, ADEC issued a first draft PSD permit and preliminary technical analysis report, concluding that Low NOx was BACT for MG-5 and MG-17. ADEC identified SCR as the most stringent technology then technically and economically feasible. ADEC nevertheless endorsed Cominco's proffered emissions-offsetting alternative of fitting MG-17 and all six existing generators with Low NOx, rather than fitting MG-5 and MG-17 with SCR. This proposal, ADEC submitted, would achieve, a maximum NOx reduction similar to the reduction SCR could achieve, and was logistically and economically less onerous for Cominco. In July 1999, EPA objected that ADEC had identified SCR as the best control technology, but failed to require it as BACT. ADEC responded with a second draft PSD permit and technical analysis report in September 1999, again finding Low NOx to be BACT for MG-17. ADEC's second draft abandoned that agency's May 1999 emissions-offsetting justification. ADEC further conceded that, lacking data from Cominco, it could make no judgment as to SCR's impact on the mine's operation, profitability, and competitiveness. It nonetheless concluded, contradicting its earlier finding that SCR was technically and economically feasible, that SCR imposed "a disproportionate cost" on the mine. In support of this conclusion, ADEC analogized the mine to a rural utility that would have to increase prices were it required to use SCR. Protesting that Cominco had not adequately demonstrated site-specific factors supporting the assertion of SCR's economical infeasibility, EPA suggested that ADEC include an analysis of SCR's adverse economic impacts on Cominco. Expressing confidentiality concerns, Cominco declined to submit financial data. In December 1999, ADEC issued a final permit and technical analysis report approving Low NOx as BACT for MG-17. Again conceding that it made no judgment as to SCR's impact on the mine's operation, profitability, and competitiveness, ADEC advanced, as cause for its decision, SCR's adverse effect on the mine's unique and continuing impact on the region's economic diversity and the venture's "world competitiveness." ADEC reiterated its rural Alaska utility analogy, and compared SCR's cost to the costs of other, less stringent, control technologies.

EPA then issued three orders to ADEC under §§ 113(a)(5) and 167 of the Act. Those orders prohibited ADEC from issuing a PSD permit to Cominco without satisfactorily documenting why SCR was not BACT for MG-17. In addition, EPA prohibited Cominco from beginning construction or modification activities at the mine, with limited exceptions. Ruling on ADEC's and Cominco's challenges to these orders, the Ninth Circuit held that EPA had authority under §§ 113(a)(5) and 167 to determine the reasonableness or adequacy of the State's justification for its BACT decision. The Court of Appeals emphasized that provision of a reasoned justification for a BACT determination by a permitting authority is undeniably a CAA "requirement." EPA had properly exercised its discretion in issuing the three orders, the Ninth Circuit held, because (1) Cominco failed to demonstrate SCR's economical infeasibility, and (2) ADEC failed to provide a reasoned justification for its elimination of SCR as a control option.

Held: CAA authorizes EPA to stop construction of a major pollutant emitting facility permitted by a state authority when EPA finds that an authority's BACT determination is unreasonable in light of 42 U.S.C. § 7479(3)'s prescribed guides. Pp. 483-502.

(a) In holding that the EPA orders constituted reviewable "final action" under § 7607(b)(1), the Ninth Circuit correctly applied Bennett v. Spear, 520 U.S. 154: To be "final," agency action must "mark the consummation of the agency's decisionmaking process," and must either determine "rights or obligations" or occasion "legal consequences," id., at 177-178. As the Ninth Circuit noted, EPA had asserted its final position on the factual circumstances underpinning the orders. If the orders survived judicial review, Cominco could not escape the practical and legal consequences of any ADEC-permitted construction Cominco endeavored. P. 483.

(b) EPA may issue a stop-construction order, under CAA §§ 113(a)(5) and 167, if a state permitting authority's BACT selection is not reasonable. Pp. 484-496.

(1) EPA has rationally construed CAA's BACT definition, 42 U. S. C. § 7479(3), and the statute's listing of BACT as a "[p]reconstruction requiremen[t]" for the PSD program, §§ 7475(a)(1) and (4), to mandate a determination of BACT faithful to the statute's definition. EPA urges that state permitting authorities' statutory discretion is constrained by § 7479(3)'s strong, normative terms "maximum" and "achievable." EPA accordingly reads §§ 113(a)(5) and 167 to empower the federal Agency to check a state agency's unreasonably lax BACT designation. In support of this reading, EPA notes that Congress intended the PSD program to prevent significant deterioration of air quality in clean-air areas. Without a federal Agency surveillance role that extends to BACT determinations, EPA maintains, this goal is unlikely to be realized. The Act's legislative history suggests that, absent national guidelines, a State deciding to set and enforce strict clean-air standards may lose existing industrial plants to more permissive States. The legislative history further suggests that without a federal check, new plants will play one State off against another with threats to locate in whichever State adopts the most permissive pollution controls. The Court agrees with EPA's reading of the statutory provisions. EPA's CAA construction is reflected in interpretive guides EPA has several times published. Although an interpretation presented in internal guidance memoranda does not qualify for dispositive force under Chevron U.S. A. Inc. v. Natural Resources Defense Council, Inc., 467 U.S. 837, 865-866, a cogent administrative interpretation nevertheless warrants respect, Washington State Dept. of Social and Health Servs. v. Guardianship Estate of Keffeler, 537 U.S. 371, 385. Pp. 484-488.

(2) ADEC's several arguments do not persuade the Court to reject as impermissible EPA's longstanding, consistently maintained interpretation. ADEC argues that CAA's BACT definition, § 7479(3), unambiguously assigns to "the permitting authority" alone the decision of the control technology qualifying as "best available." In ADEC's view, EPA's enforcement role is restricted to assuring that the permit contain a BACT limitation. CAA entrusts state authorities with initial responsibility to make BACT determinations because they are best positioned to adjust for local circumstances that might make a technology "unavailable" in a particular area. According state authorities...

To continue reading

Request your trial
562 cases
  • Oceana, Inc. v. Evans
    • United States
    • U.S. District Court — District of Columbia
    • August 2, 2005
    ...upset the decision on that account `if the agency's path may reasonably be discerned.'" See Alaska Dep't of Envtl. Conservation v. EPA, 540 U.S. 461, 497, 124 S.Ct. 983, 157 L.Ed.2d 967 (2004) (quoting Bowman Transp., Inc. v. Arkansas-Best Freight Sys., Inc., 419 U.S. 281, 286, 95 S.Ct. 438......
  • Royster-Clark Agribusiness, Inc. v. Johnson
    • United States
    • U.S. District Court — District of Columbia
    • August 29, 2005
    ...construction of proposed modifications); Alaska Dept. of Envtl. Conserv. v. EPA, 244 F.3d 748 (9th Cir.2001), aff'd, 540 U.S. 461, 124 S.Ct. 983, 157 L.Ed.2d 967 (2004) (same). But these latter cases are of no help, for unlike a compliance order, a NOV does not order plaintiffs to stop work......
  • Horizon Lines, LLC. v. U.S.
    • United States
    • U.S. District Court — District of Columbia
    • February 10, 2006
    ...be prevented, no clause, sentence, or word shall be superfluous, void, or insignificant." Alaska Dep't of Envtl. Conservation v. E.P.A., 540 U.S. 461, 489 n. 13, 124 S.Ct. 983, 157 L.Ed.2d 967 (2004) (internal quotation marks and citations omitted). (Pl.'s Mot. at The Court agrees that Cust......
  • Norton v. Beasley
    • United States
    • U.S. District Court — Eastern District of Kentucky
    • September 30, 2021
    ...not upset the decision on that account ‘if the agency's path may be reasonably discerned.’ " Alaska Dep't of Env't Conservation v. EPA , 540 U.S. 461, 497, 124 S.Ct. 983, 157 L.Ed.2d 967 (2004) (quoting Bowman Transp., Inc. v. Arkansas—Best Freight System, Inc. , 419 U.S. 281, 286, 95 S.Ct.......
  • Request a trial to view additional results
23 books & journal articles
  • Union of Concerned Scientists v. Pruitt: Can EPA Purge Its Academic Science Advisors?
    • United States
    • Environmental Law Reporter No. 48-7, July 2018
    • July 1, 2018
    ...Id . at 2127. 40. 551 U.S. 644, 37 ELR 20153 (2007). 41. Id . at 655; 16 U.S.C. §§1531-1544; ELR Stat. ESA §§2-18. 42. Id . at 659. 43. 540 U.S. 461, 502, 34 ELR 20012 (2004); 42 U.S.C. §§7401-7671q; ELR Stat. CAA §§101-618. 44. Id . at 498. 45. Id . at 502. 46. See , e.g. , Judulang v. Hol......
  • Civil Enforcement of the Clean Air Act
    • United States
    • Air pollution control and climate change mitigation law
    • August 18, 2010
    ...2d 739 (N.D. Ohio 2000). 208. 125 F. Supp. 2d 1050, 31 ELR 20335 (D. Colo. 2000). 209. 269 F.3d 1003, 32 ELR 20218 (9th Cir. 2001). 210. 540 U.S. 461 (2004) (the Red Dog Mine Case). 211. 481 U.S. 412 (1987). Virginia denied the petitioner’s request for a jury trial, concluding that Tull had......
  • DISORDERED LAW: OBAMA TO TRUMP EXECUTIVE BRANCH ORDERS MANDATING NON-ENFORCEMENT OF INTERNATIONAL TREATIES.
    • United States
    • Albany Law Review Vol. 85 No. 2, June 2022
    • June 22, 2022
    ...Coeur Alaska, Inc. v. Southeast Alaska Conservation Council, 557 U.S. 261, 284 (2009); see Alaska Dep't of Env't Conservation v. EPA, 540 U.S. 461, 487 (2004) (Chevron deference did not apply; Mead analysis and (275) Skidmore v. Swift & Co., 323 U.S. 134 (1944). (276) United States v. M......
  • Controlling Global Climate Change
    • United States
    • Air pollution control and climate change mitigation law
    • August 18, 2010
    ...Review: Should It Survive ?, 34 ELR 10673 (July 2004). 653. CAA §169(3), 42 U.S.C. §7479(3). See Alaska Dep’t Envtl. Conservation v. EPA, 540 U.S. 461, 471-73. he U.S. Supreme Court upheld EPA’s use of a cost-beneit analysis to determine the best technology under the Clean Water Act’s eluen......
  • Request a trial to view additional results

VLEX uses login cookies to provide you with a better browsing experience. If you click on 'Accept' or continue browsing this site we consider that you accept our cookie policy. ACCEPT