Alaska Wilderness League v. United States Environmental Protection Agency
727 F.3d 934
9th Cir.
2013
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Docket

ALASKA WILDERNESS LEAGUE; Center for Biological Diversity; Natural Resources Defense Council; Northern Alaska Environmental Center; Pacific Environment; Resisting Environmental Destruction On Indigenous Lands; Sierra Club; The Wilderness Society, Petitioners, v. UNITED STATES ENVIRONMENTAL PROTECTION AGENCY, Respondent, Shell Offshore Inc., Respondent-Intervenor.

No. 12-71506.

United States Court of Appeals, Ninth Circuit.

Argued and Submitted May 21, 2013. Filed Aug. 15, 2013.

727 F.3d 934

public. See (upholding sentence and noting the “need to deter recidivism and protect the public“); (citing defendant‘s “undeterred recidivism” to support the reasonableness of his sentence). Finally, Grant offered very little by way of mitigation during her sentencing, simply invoking, as she had previously, her need to provide for her family. The record plainly shows that the district court made several references to Grant‘s family obligations and specifically reasoned that it could not allow Grant‘s family to become her “license to flout the law [and] flout the regulations.” Thus, Grant‘s sentence was substantively reasonable.

CONCLUSION

The record demonstrates Grant‘s fugitive status. As such, the Revocation Hearing fell within Grant‘s Probation Term, and the district court had jurisdiction to revoke Grant‘s probation. Further, the district court did not abuse its discretion in sentencing Grant.

AFFIRMED.

ALASKA WILDERNESS LEAGUE; Center for Biological Diversity; Natural Resources Defense Council; Northern Alaska Environmental Center; Pacific Environment; Resisting Environmental Destruction On Indigenous Lands; Sierra Club; The Wilderness Society, Petitioners, v. UNITED STATES ENVIRONMENTAL PROTECTION AGENCY, Respondent, Shell Offshore Inc., Respondent-Intervenor.

Colin C. O‘Brien (briefed and argued), Earthjustice, Anchorage, AK; Eric P. Jorgensen, Earthjustice, Juneau, AK, for Petitioners.

Ignacia S. Moreno and Angeline Purdy (briefed and argued), Assistant Attorneys General, United States Department of Justice, Environment and Natural Resources Division; Alexander Fidis, Office of Regional Counsel, Region 10, United States Environmental Protection Agency; David Coursen, Office of General Counsel, United States Environmental Protection Agency, for Respondent.

Duane A. Siler, Sarah C. Bordelon, and Tony G. Mendoza, Crowell & Moring LLP, Washington, D.C.; Kathleen M. Sullivan (briefed and argued), William B. Adams, and David S. Mader, Quinn Emanuel Urquhart & Sullivan, LLP, New York, NY, for Respondent-Intervenor.

Samuel B. Boxerman, Jim Wedeking, and Lisa E. Jones, Sidley Austin, LLP, Washington D.C.; Mara E. Zimmerman, American Petroleum Institute, Washington, D.C., for Amicus Curiae American Petroleum Institute.

Cameron M. Leonard, Senior Assistant Attorney General, Office of the Attorney General of Alaska, Fairbanks, AK, for Amicus Curiae State of Alaska.

Before: A. WALLACE TASHIMA, RICHARD C. TALLMAN, and N. RANDY SMITH, Circuit Judges.

OPINION

N.R. SMITH, Circuit Judge:

42 U.S.C. § 7661c(e) is ambiguous as to whether “increment” requirements are “applicable” to a temporary source like Shell Offshore, Inc.‘s (“Shell“) drill vessel Kulluk. Accordingly, we defer to the EPA Environmental Appeals Board‘s (“EAB“) reasonable interpretation of § 7661c(e). See . The EAB reasonably concluded that Shell need not analyze the Kulluk‘s potential impact on increment before obtaining an oil exploration permit. We also deny the petition for review of the Environmental Protection Agency‘s (“EPA“) exemption of a 500-meter radius surrounding the Kulluk from ambient air quality standards, because the decision was “a permissible application of the EPA‘s regulations.” See .

FACTS AND PROCEDURAL HISTORY

A. Statutory and Regulatory Background

The Clean Air Act (the “Act“) imposes responsibility on both federal and state regulators to control and improve the nation‘s air quality. (citing 42 U.S.C. §§ 7401-7671q). “The Act requires states to submit for the EPA‘s approval a state implementation plan [‘SIP‘] that provides for attainment and maintenance of the national ambient air quality standards (‘NAAQS‘) promulgated by the EPA.” Id. Title V of the Act, 42 U.S.C. §§ 7661-7661f, requires certain sources, including sources operating only temporarily in a given location, to obtain permits to assure compliance with the Act. See 42 U.S.C. § 7661c.

In “clean air areas,” the Act imposes additional preconstruction permitting requirements under the Prevention of Significant Deterioration program (the “PSD“). (citing 42 U.S.C. §§ 7470-7492). The PSD imposes increment standards to maintain air quality in clean air areas by preventing the total pollution from exceeding a certain level over an established baseline for the given region. See . Temporary sources may be subject to increment standards under 42 U.S.C. § 7661c(e), which reads, in pertinent part:

The permitting authority may issue a single permit authorizing emissions from similar operations at multiple temporary locations. No such permit shall be issued unless it includes conditions that will assure compliance with all the requirements of this chapter at all authorized locations, including, but not limited to, ambient standards and compliance with any applicable increment or visibility requirements under part C of subchapter I of this chapter.

At issue here is whether there are increment requirements “applicable” to the Kulluk under § 7661c(e) and the PSD.

Also relevant to this appeal, the Act requires the EPA to regulate, through national quality standards, “ambient air,” “which is the statute‘s term for the outdoor air used by the general public.” . EPA-promulgated regulations define “ambient air” as “that portion of the atmosphere, external to buildings, to which the general public has access.” 40 C.F.R. § 50.1(e). Interpreting these statutes and regulations, the EPA has long exempted from the definition of ambient air “the atmosphere over land owned or controlled by the source and to which public access is precluded by a fence or other physical barriers.” Letter from Douglass M. Costle, EPA Administrator, to Senator Jennings Randolph, Chairman of the Environment and Public Works Committee (Dec. 19, 1980) (the “Costle Letter“).

B. EPA‘s Grant of Shell‘s Permit and Alaska Wilderness‘s Challenge

To comply with Title V, Shell sought and obtained three related permits in 2011. At Shell‘s request, the EPA subsequently consolidated the permits into one permitting document (the “Permit“). The Permit allows Shell to construct, operate, and conduct “pollutant emitting activities” associated with the Kulluk in the Beaufort Sea off Alaska‘s North Slope. Before issuing the Permit, the EPA released a Statement of Basis. The Statement of Basis provided that the EPA would not require Shell to analyze the effect its emissions would have on the increment for the Kulluk‘s area of operation. During the public comment period on the Permit, commenters took issue with this decision and the EPA‘s rationale in the Statement of Basis. The EPA‘s Response to Comments, issued contemporaneously with the Permit, addressed these concerns. The EPA concluded that increment analysis was unnecessary, because, under § 7661c(e) and the other relevant statutes, no increment requirements were “applicable” to the Kulluk.

The Permit and Response to Comments also announced the EPA‘s decision to grant Shell‘s requested exemption of 500 meters surrounding the Kulluk from “ambient air” regulations. The Permit conditioned the exemption on the establishment of a U.S. Coast Guard “safety zone” and a “public access control program” to restrict public access to the waters within 500 meters of the Kulluk.

Alaska Wilderness raised the increment and ambient air issues, among others, in its challenge of the Permit before the EAB. Alaska Wilderness contended that the EPA misinterpreted “applicable increment” under § 7661c(e). Alaska Wilderness argued that EPA‘s “source-based” interpretation erred by applying increment standards to temporary sources only if the PSD would impose increment standards on a similar stationary source. Alaska Wilderness maintained a “geography based” interpretation—that increment requirements are “applicable” to all sources any time they are established for the geographic area. Alaska Wilderness also argued that the “ambient air” exemption was inconsistent with the Costle Letter, because Shell did not own and could not, by physical barrier, exclude the public from accessing the space. In a 100-page decision (the “EAB Decision“), the EAB rejected both challenges. With respect to the increment issue, the EAB held:

Increments ... are not directly imposed by [§ 7661c(e)]. Instead, they must be implemented (i.e., applied to a source) through either of two means: (1) a state implementation plan, per [§ 7471] and 40 C.F.R. § 51.166(a)(1); or (2) the PSD major source permitting program, per [§ 7475(a)(3)(A)] and 40 C.F.R. § 52.21. Thus, while [§ 7661c(e)] can serve as the direct source of NAAQS compliance requirements and other [Clean Air Act] requirements for temporary sources, it only imposes PSD increment requirements to the extent such requirements are “applicable” to the source.

Alaska Wilderness‘s timely petition (the “Petition“) for review of the EAB Decision followed.

STANDARD OF REVIEW

As a threshold matter, we reject Alaska Wilderness‘s argument that the EAB Decision is not entitled to Chevron deference. “[Chevron] generally sets forth the framework by which we review an agency‘s interpretation of a statute.” . ”Chevron deference is appropriate where the agency can demonstrate that it has the general power to make rules carrying the force of law and that the challenged action was taken in exercise of that authority.” Id. at 962 (internal quotation marks omitted).

Here, “Congress explicitly granted to the EPA the authority to promulgate regulations and grant air permits” for the Kulluk‘s operating region. . The EPA exercised its “authority through a formal process that included ... public notice and comment ... and [a] reasoned EAB decision[] upholding the air permits at issue.” Id. As we have already held in REDOIL, the EAB proceeding was “a formal adjudication that warrants Chevron deference.” Id.

“Under [Chevron‘s two-step] framework at the first step we determine ‘whether Congress has directly spoken to the precise question at issue. If the intent of Congress is clear, that is the end of the matter; for the court as well as the agency, must give effect to the unambiguously expressed intent of Congress.‘” (quoting ). “[I]f the statute is silent or ambiguous with respect to the specific issue, the question for the court is whether the agency‘s answer is based on a permissible construction of the statute.” Id. at 962.

DISCUSSION

A. Increment

The parties do not dispute that the Kulluk is a “major source” under Title V and, thus, subject to that title‘s permitting requirements. Further, the parties agree that our analysis of § 7661c(e) must focus on the EPA‘s interpretation of “applicable increment ... requirements.” It is also undisputed that the Kulluk is not a “major emitting facility” under the PSD. See 42 U.S.C. § 7479(1). If it were, then the parties agree that 42 U.S.C. § 7475(a)(3)(A) would require a preconstruction increment analysis under the EPA‘s interpretation set forth in the EAB Decision.

Although the Kulluk is not a “major emitting facility,” Alaska Wilderness argues that § 7661c(e) (and the other relevant statutes) unambiguously support its position. Alaska Wilderness argues that § 7661c(e) mandated a preconstruction increment analysis for the Kulluk, because increments have been established for the Kulluk‘s operating region. The EPA maintains that § 7661c(e) did not require an increment analysis for the Kulluk. The EPA argues that whether increment requirements are “applicable” under § 7661c(e) (which incorporates the PSD by reference) is a function not only of geography, but also a function of whether the PSD would require an increment analysis for the specific source if it were stationary. Thus, EPA argues, the Kulluk does not trigger the analysis requirement, which the PSD imposes only if required by the state SIP or if the source is a “major emitting facility” under 42 U.S.C. § 7475.

1. Chevron Step One

A statute is ambiguous if it is susceptible to more than one reasonable interpretation. See ; ; see also (“A statute is ambiguous if Congress has not directly spoken to the precise question at issue.” (internal quotation marks omitted)). “The plainness or ambiguity of statutory language is determined by reference to the language itself, the specific context in which that language is used, and the broader context of the statute as a whole.” . Accordingly, we “begin with the plain language of the statute.” .

Section 7661c(e) is ambiguous in its use of the term “applicable.” To give content to this term, Section 7661c(e) expressly incorporates and relies on “Part C of subchapter I of [Chapter 85].” 42 U.S.C. § 7661c(e). One Part C provision, 42 U.S.C. § 7473, sets forth increment standards generally and makes clear that permissible increment levels are established by geographic area. However, § 7473 does not specify how increments apply to minor, temporary sources like the Kulluk. Section 7473 is also silent as to preconstruction increment analysis and imposes no preconstruction requirements on any source. As such, Alaska Wilderness cannot rely on § 7473 to support its argument that § 7661c(e) unambiguously compels a geography-based reading of the term “applicable.”

Two other Part C provisions impose increment requirements based on source rather than geography. First, 42 U.S.C. § 7471 incorporates any increment requirements set forth in the governing SIP, making clear that they apply to the sources covered under those state plans. Second, 42 U.S.C. § 7475(a)(3)(A) imposes increment analysis requirements on “major emitting facilities.” Under these sections, and Alaska‘s SIP, no increment requirement would apply to a minor PSD source like the Kulluk if it were stationary. Accordingly, because Part C provisions support a source-based reading of “applicable,” but allowable increment levels are determined by geographic area, § 7661c(e) is ambiguous.1

We reject Alaska Wilderness‘s argument that the EPA‘s interpretation renders the different permitting provision of § 7661c(a) absurd or superfluous by redundantly applying state SIP requirements. Section 7661c(a), with a broad brush, states that any permit must include conditions to assure compliance with the requirements of the chapter, including SIP requirements. Section 7661c(e) performs a more specific function—setting forth which requirements apply to temporary sources. As such, § 7661c(e) does not duplicate § 7661c(a), even under the EPA‘s reading. In fact, using Alaska Wilderness‘s logic, § 7661c(e)‘s incorporation of any portion of Part C would be redundant, because Part C is already part of the “chapter” covered by § 7661c(a). Clearly this is not the case. Thus, § 7661c(a)‘s reference to SIPs does not foreclose the EPA‘s interpretation, and Alaska Wilderness cannot resort to § 7661c(a) to clarify § 7661c(e)‘s ambiguity.

2. Chevron Step Two

If an agency interprets an ambiguous statute and “fills a gap or defines a term in a way that is reasonable in light of the legislature‘s revealed design, we give [that] judgment controlling weight.” (alteration in original) (internal quotation marks omitted). Here, the EPA‘s interpretation is consistent with Congress‘s “revealed design” as evidenced by § 7661c(e)‘s plain language.2 In fact, the EPA arguably proffers the more reasonable reading of § 7661c(e) and Part C, given § 7471‘s and § 7475(a)(3)(A)‘s imposition of increment analysis requirements by source, and given the absence of any such requirement imposed by area under § 7473. Thus, we defer to the EPA‘s reasonable interpretation.

B. Ambient Air

Since briefing was completed in this case, we decided REDOIL. We then invited the parties to submit supplemental briefs as to the effect of REDOIL on the ambient air issue in this case. After briefing, we agree with the parties that REDOIL directly controls this issue. Thus, as in REDOIL, we conclude that the EPA‘s exemption of a 500-meter radius surrounding the Kulluk from ambient air quality standards was “a permissible interpretation of its ambient air regulation and earlier letter ruling.” .

CONCLUSION

Section 7661c(e) is ambiguous, and the EPA‘s interpretation is reasonable under the applicable statutes’ plain language. Thus, we owe Chevron deference to the EAB Decision not to require a preconstruction increment analysis for the Kulluk. Similarly, as we held in REDOIL, the EPA permissibly granted a 500-meter exemption to the Kulluk from “ambient air” standards.

PETITION DENIED.

Notes

1
Section 7661c(e)‘s express reliance on Part C demonstrates that we cannot, as Alaska Wilderness urges, read § 7661c(e) to unambiguously impose increment requirements over and above those created by Part C. By contrast, the parties do not dispute that § 7661c(e) imposes substantive NAAQS requirements on temporary sources. However, this does not support Alaska Wilderness‘s increment argument; it only demonstrates the section‘s ambiguity. The NAAQS that § 7661c(e) references do not incorporate another provision like Part C to determine which requirements are “applicable.” Thus, Part C‘s failure to clarify the interplay between geography and source brings ambiguity to § 7661c(e)‘s reference to increment, but has no bearing on the NAAQS.
2
Alaska Wilderness cannot rely on § 7661c(e)‘s legislative history to support its argument that § 7661c(e) unambiguously compels its geography-based interpretation. Any attempt to invoke § 7661c(e)‘s legislative history is inconsistent with Alaska Wilderness‘s claim that the statute is unambiguous. If the statutory language were truly as clear as Alaska Wilderness argues, “reference to the legislative history would be both unnecessary and inappropriate to illuminate unambiguous text.” .
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