Eagle-Picher Industries, Inc. v. United States Environmental Protection Agency

759 F.2d 905, 245 U.S. App. D.C. 179, 15 Envtl. L. Rep. (Envtl. Law Inst.) 20467, 22 ERC (BNA) 1657, 1985 U.S. App. LEXIS 28852
Court of Appeals for the D.C. Circuit·Decided April 16, 1985·No. Nos. 83-2259 to 83-2264, 83-2266·Published·Cited by 9 cases

Opinion

Opinion for the Court by HARRY T. EDWARDS, Circuit Judge.

HARRY T. EDWARDS, Circuit Judge:

In this case, the petitioners challenge the legality of the Hazardous Ranking System (“HRS”), adopted by the Environmental Protection Agency (“EPA” or the “agency”) pursuant to section 105 of the Comprehensive Environmental Response, Compensation and Liability Act of 1980 (“CERCLA”).1 The HRS is the designated model used by the EPA to determine sites to be listed on a National Priority List (“NPL”) under CERCLA. The NPL lists 400 sites that have been contaminated by harmful substances and that may warrant corrective action under CERCLA. Petitioners here claim that they should not have been included on the NPL because the ranking methodology established by the HRS is unlawful.2

The HRS was promulgated on July 16, 1982, in a notice-and-comment rulemaking proceeding separate from that which produced the final NPL on September 8, 1983. CERCLA’s statutory review provision, section 113(a),3 stipulates that petitions for judicial review of regulations pro[183]*183mulgated under CERCLA must be filed with this court within ninety days of the regulations’ promulgation. The petitioners failed to seek review of the HRS during the mandated statutory period. Despite their untimely request for review, the petitioners urge that their failure tó file within the statutory period should be excused because they assumed that their challenge was not ripe for review until the NPL was promulgated. We reject this argument as patently untenable under the applicable terms of CERCLA.

We emphasize first that petitioners who delay filing requests for review on their own assessment of when an issue is ripe for review do so at the risk of finding their claims time-barred. Normally, the appropriate time for a judicial determination of the ripeness of an issue is within the prescribed statutory period for review. In general, we will refuse to hypothesize whether, in retrospect, a claim would have been deemed ripe for review had it been brought during the statutory period, in order to save an untimely claim. Exceptions occasionally may be justified in the light of changed circumstances giving rise to a new cause of action beyond the statutory period for review; compelling case precedent that makes it clear beyond doubt that the claim was not ripe during the statutory period; or clear evidence that a failure to consider a petitioner’s claims would work a manifest injustice. The petitioners’ challenge to the HRS fall within none of these exceptions. However, because we articulate here for the first time the circumstances under which the court will engage in “retrospective ripeness analysis” after the statutory review period has expired, we proceed to evaluate the petitioners’ claim on the merits.

We conclude that the challenge to the HRS was ripe during the statutory review period. Therefore, we find petitioners’ claim to be barred as untimely. In the alternative, we hold on the merits that, given the narrow purpose of the HRS and the NPL — to provide an expeditious and relatively inexpensive initial determination of which sites may warrant further action under CERCLA — and in light of the agency’s manifest awareness of the HRS’s technical limitations, the model is reasonable and consistent with congressional intent.

I. Background

Through CERCLA, Congress sought to establish a system for rectifying some of the serious public health and environmental problems that have been caused by improper disposal of hazardous wastes, pollutants and contaminants. Essentially, CERCLA authorizes the EPA to respond to actual or threatened releases of these harmful substances,4 both through removal actions, which entail the actual cleanup of a release,5 and remedial actions, which provide for remedies to prevent or minimize the release of hazardous substances.6 The statute also establishes a fund (the “Superfund”) to pay for cleanup action.7

In section 1058 of CERCLA, Congress instructs the EPA9 to revise the National Contingency Plan (“NCP”), which had originally been developed under the Clean Water Act10 to give guidance to agencies in removing oil or hazardous substances from United States waters, to “reflect and effectuate the responsibilities and powers” created by CERCLA. This revision is to in-[184]*184elude “criteria for determining priorities among releases or threatened releases throughout the United States____”11 The EPA is also directed to include in the NCP an initial list of at least 400 sites selected on the basis of the above criteria — the NPL. The statute requires that the NPL be revised “no less often than annually.” 12

In response to this statutory mandate, the EPA adhered to the requisites of notice-and-comment rulemaking and published a proposed revision of the NCP in the Federal Register on March 12, 1982.13 This proposal explicitly designated the HRS as the method favored by the agency for ranking hazardous substance releases, included an address where the HRS could be obtained upon request, and solicited comment on the HRS.14 Numerous comments on the proposed HRS were received and considered by the EPA during the rulemaking process. The final versions of the revised NCP and the HRS were then promulgated on July 16, 1982, and published in the Federal Register.15

As the EPA explained in the preamble to the final NCP, “the HRS is designed to estimate the potential hazard presented by releases or threatened releases of hazardous substances, pollutants and contaminants.” 16 The agency applies the HRS to data from an observed or potential release to obtain a “score” or estimate of the risk from the release. The EPA then relies on HRS scores to determine which releases should be listed on the NPL.17

The HRS score is calculated by analyzing three potential “pathways” of human or environmental exposure: (1) ground water, (2) surface water, and (3) air. Within each of these pathways, the HRS takes account of three categories of factors “that are designed to encompass most aspects of the likelihood of exposure to a hazardous substance through a release and the magnitude or degree of harm from such exposure.” 18 These categories reflect: “(1) [t]he existence or likelihood of a release, (2) the characteristics of the hazardous substances that have been or may be released, and (3) the population or sensitive environment that is threatened.” 19

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Eagle-Picher Industries, Inc. v. United States Environmental Protection Agency, 759 F.2d 905, 245 U.S. App. D.C. 179, 15 Envtl. L. Rep. (Envtl. Law Inst.) 20467, 22 ERC (BNA) 1657, 1985 U.S. App. LEXIS 28852 (D.C. Cir. 1985).

759 F.2d 905 (Eagle-Picher Industries, Inc. v. United States Environmental Protection Agency) — published by Counsel Stack Legal Research, free access to 12M+ legal documents.

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