Natural Resources Defense Council, Inc. v. Lee M. Thomas, Administrator, U.S. Environmental Protection Agency, Alabama Power Co., Intervenor

845 F.2d 1088, 269 U.S. App. D.C. 343, 18 Envtl. L. Rep. (Envtl. Law Inst.) 20955, 27 ERC (BNA) 1572, 1988 U.S. App. LEXIS 5853, 1988 WL 40249
Court of Appeals for the D.C. Circuit·Decided May 3, 1988·No. 86-1305·Published·Cited by 20 cases

Opinions

Opinion for the Court filed by Circuit Judge SENTELLE.

Concurring opinion filed by Circuit Judge HARRY T. EDWARDS.

SENTELLE, Circuit Judge:

This case involves a petition by a public interest environmental group, National Resources Defense Council, Inc. (NRDC), to have this Court review the choice of the Administrator of the Environmental Protection Agency (EPA) between two monitoring methods in enforcing the National Ambient Air Quality Standards (NAAQS) for sulfur oxides. On the Court’s last occasion to consider the Administrator’s choice some seven years ago, the Court held it could not address the issue unless and until the EPA did so first in a “properly noticed rulemaking.” PPG Industries, Inc. v. Costle, 659 F.2d 1239 (D.C.Cir.1981). While the posture of the present petition differs from that of the one before the Court in PPG Industries, the fundamental principles of judicial review of administrative proceedings have not changed, such a rule-making has not yet occurred, and the result, or non-result, must be . the same. We will, therefore, for the reasons set out below, dismiss the petition and once again make no determination on the merits of either method of monitoring.

Background

While the statutory and administrative landscape upon which the present controversy stands was painted in some detail by Judge Bazelon in the PPG Industries decision, supra, some further sketching of the terrain is necessary to an understanding of this decision. Since the enactment of the [1090] Clean Air Amendments of 1970, Pub.L. No. 91-604, 84 Stat. 1676,1 the EPA has been the federal component in a system of shared federal and state responsibility for reducing air pollution. Under §§ 108 and 109 of the Clean Air Act, 42 U.S.C. §§ 7408-09, the EPA is charged with identifying air pollutants that endanger the public health and welfare, and formulating NAAQS that specify the maximum permissible concentrations of these pollutants in the ambient air. See Train v. NRDC, 421 U.S. 60, 64-65, 95 S.Ct. 1470, 1474-75, 43 L.Ed.2d 731 (1975). Each state has nine months from the promulgation of an ambient air quality standard to adopt a “state implementation plan” (SIP) and submit the plan to EPA for approval. 42 U.S.C. § 7410. Each state has the right to adopt and enforce its own standards regarding emissions of air pollutants provided such state standard is no less stringent than any applicable federally mandated SIP provision.

In 1971, the EPA promulgated a series of NAAQS for sulfur oxides, measured as sulfur dioxide. These standards established maximum acceptable average concentrations for one year periods, 24-hour periods, and 3-hour periods. Any locality in which the concentration exceeds the allowable maximum for either 3-hour or 24-hour periods more than once during a year is subject to remedial restrictions under the Act. There are two basic types of analysis for determining average concentrations in air samples. The “block average” method involves averaging the pollutant concentrations in the air samples for non-overlapping periods, typically midnight to midnight in the case of the 24-hour averages, resulting in 365 separate averages per calendar year,2 and 8 times that many or 2,920 3-hour averages.3 The “running average” method involves continuous averaging of overlapping 24-hour periods (or 3-hour periods) and is designed to detect concentrations exceeding the allowable limits for 24-hour periods crossing midnight, which would not otherwise be discerned in an averaging method focusing on either of the two calendar days during which a portion of the exceedance occurred.4 Obviously, an infinite number of such running average periods per year is possible, since the averaging could begin at intervals of one hour, one-half hour, one minute, one second, or theoretically, an infinitesimally small interval. However, no one contends here, or has contended throughout the protracted history of this controversy, that intervals smaller than one hour should be employed so that the running average method NRDC champions before us would result in 24 times as many daily averages as the block average method NRDC opposes.

From the promulgation of the sulfur oxide NAAQS in 1971 until 1977, the EPA interpreted the NAAQS as allowing compliance through block averaging. In 1977, the Office of Air Quality Planning and Standards recommended the use of running averages.5 Thereafter in 1979, EPA promulgated monitoring rules requiring running averages. In 1981 in PPG Industries, supra, because of the Agency’s failure to give adequate notice of the change in its long standing practice, we invalidated those rules. However, we did not require any rulemaking on the subject nor require the use by the EPA of either method of averaging but rather directed: “If on remand EPA wishes to require the reporting of running averages, it should conduct notice and comment proceedings to consider and explain its decision properly.” Id. at 1250 (emphasis supplied).

[1091] The EPA conducted no rulemaking but continued the historic practice of permitting the use of the less stringent block average method while contemporaneously permitting the newer and more exacting running average.

NRDC, based on subsequent events, a further discussion of which will appear in the body of this opinion, contends that the question .is now ripe for review. The EPA contends that this Court is still as much in need of a fuller administrative record for review as it was in 1981 and that the petition should, therefore, be dismissed. The EPA’s objections are based in the related arguments of lack of ripeness and final agency decision which we will discuss in turn.

Analysis

Because the questions of ripeness and final agency action are inextricably intertwined, some facts discussed under each heading will necessarily bear relevance to the other; but for convenience of understanding, we will set them out separately, together with subdivisions where necessary and appropriate.

A. Ripeness

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Natural Resources Defense Council, Inc. v. Lee M. Thomas, Administrator, U.S. Environmental Protection Agency, Alabama Power Co., Intervenor, 845 F.2d 1088, 269 U.S. App. D.C. 343, 18 Envtl. L. Rep. (Envtl. Law Inst.) 20955, 27 ERC (BNA) 1572, 1988 U.S. App. LEXIS 5853, 1988 WL 40249 (D.C. Cir. 1988).

845 F.2d 1088 (Natural Resources Defense Council, Inc. v. Lee M. Thomas, Administrator, U.S. Environmental Protection Agency, Alabama Power Co., Intervenor) — published by Counsel Stack Legal Research, free access to 12M+ legal documents.

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