Edison Electric Institute v. U.S. Environmental Protection Agency

996 F.2d 326, 302 U.S. App. D.C. 60, 23 Envtl. L. Rep. (Envtl. Law Inst.) 21006, 36 ERC (BNA) 1913, 1993 U.S. App. LEXIS 14493
CourtCourt of Appeals for the D.C. Circuit
DecidedJune 18, 1993
Docket91-1586
StatusPublished
Cited by71 cases

This text of 996 F.2d 326 (Edison Electric Institute v. U.S. Environmental Protection Agency) is published on Counsel Stack Legal Research, covering Court of Appeals for the D.C. Circuit primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Edison Electric Institute v. U.S. Environmental Protection Agency, 996 F.2d 326, 302 U.S. App. D.C. 60, 23 Envtl. L. Rep. (Envtl. Law Inst.) 21006, 36 ERC (BNA) 1913, 1993 U.S. App. LEXIS 14493 (D.C. Cir. 1993).

Opinion

Opinion for the court filed by Circuit Judge BUCKLEY.

BUCKLEY, Circuit Judge:

Three national electric utility associations and seventy-three individual power companies petition for review of the Environmental Protection Agency’s interpretation of section 3004® of the Resource Conservation and Recovery Act, a provision that governs the storage of hazardous wastes. The EPA’s interpretation renders it unlawful to store wastes for indefinite periods pending the development of adequate treatment techniques or disposal capacity. Petitioners contend that this interpretation is both inconsistent with the statute and unreasonable as applied to generators of wastes containing both hazardous and radioactive components, for which there are currently few lawful treatment or disposal options. Because we find that the EPA’s interpretation is not only permissible, but is in fact mandated by the terms of the statute, we deny the petition.

I. BACKGROUND

The Resource Conservation and Recovery Act of 1976 (“RCRA”) establishes a comprehensive “cradle-to-grave” scheme for regulating hazardous wastes. As amended by the Hazardous and Solid Waste Amendments of 1984 (“HSWA”), the centerpiece of RCRA is an ambitious set of land disposal restrictions (“LDRs”). The LDRs prohibit land disposal of particular wastes as of specified dates unless-such disposal is carried out in accordance with regulations issued by the EPA. See generally Chemical Waste Management, Inc. v. EPA 976 F.2d 2, 7-9 (D.C.Cir.1992). For most wastes, land disposal may continue after the applicable deadline only if one of two conditions is met. First, land disposal of a waste is allowable if the EPA concludes, with “a reasonable degree of certainty, that there will be no migration of hazardous constituents from the disposal unit or injection zone for as long as the waste® remain[s] hazardous.” 42 U.S.C. § 6924(d)(1). Second, a waste may be land disposed if that waste is treated in accordance with standards established by the EPA. Id. § 6924(m)(2). Thus, RCRA directs the EPA to

promulgate regulations specifying those levels or methods of treatment, if any, which substantially diminish the toxicity of the waste or substantially reduce the likelihood of migration of hazardous constituents from the waste so that short-term and *329 long-term threats to human health and the environment are minimized.

Id. § 6924(m)(l).

The provision of RCRA at issue here, section 3004(j), limits the storage of hazardous wastes. It provides:

In the case of any hazardous waste which is prohibited from one or more methods of land disposal under this section (or under regulations promulgated by the Administrator under any provision of this section) the storage of such hazardous waste is prohibited unless such storage is solely for the purpose of the accumulation of such quantities of hazardous waste as are necessary to facilitate proper recovery, treatment or disposal.

Id. § 6924(j). Congress enacted this section because it “believed that permitting storage of large quantities of waste as a means of forestalling required treatment would involve health threats equally serious to those posed by land disposal, and therefore opted in large part for a ‘treat as you go’ regulatory regime.” Hazardous Waste Treatment Council v. EPA 886 F.2d 355, 357 (D.C.Cir.1989) (“HWTC III”).

At issue in the present case is the application of section 3004(j) and the EPA’s implementing regulations to “mixed wastes.” Mixed wastes are wastes that contain both a hazardous waste component regulated under RCRA and a radioactive waste component regulated under the Atomic Energy Act (“AEA”). See State Authorization To Regulate the Hazardous Components of Radioactive Mixed Wastes Under the Resource Conservation and Recovery Act, 51 Fed.Reg. 24,504 (1986) (announcing the EPA’s determination “that wastes containing both hazardous waste and radioactive waste are subject to the RCRA regulation”); New Mexico v. Watkins, 969 F.2d 1122, 1132 (D.C.Cir.1992) (deferring to the EPA’s conclusion that RCRA applies to mixed wastes). These wastes are generated by nuclear power plants, as well as by universities, research institutions, hospitals, and industrial facilities. At the present time, adequate treatment'methods have not been developed, and there is a severe shortage of disposal capacity for mixed wastes. As a result, generators have turned to storing these wastes as their only available option short of ceasing their operations or engaging in illegal disposal practices.

The EPA issued regulations to implement section 3004(j) in 1986. See Hazardous Waste Management System; Land Disposal Restrictions, 51 Fed.Reg. 40,572, 40,579, 40,-642-43 (1986). Reiterating the statutory language, the regulations provided that generators were permitted to store hazardous wastes subject to the LDRs in “tanks or containers on-site” if such storage was “solely for the purpose of the accumulation of such quantities of hazardous waste as necessary to facilitate proper recovery, treatment, or disposal....” 40 C.F.R. § 268.50(a)(1) (1992). The regulations also established a burden-shifting scheme for determining when storage would be viewed as “solely for the purpose of the accumulation of such quantities of hazardous waste as necessary to facilitate proper recovery, treatment, or disposal.” Specifically, the regulations provided:

(b) An owner/operator of a treatment, storage or disposal facility may store such wastes for up to one year unless the Agency can demonstrate that such storage was not solely for the purpose of accumulation of such quantities of hazardous waste as are necessary to facilitate proper recovery, treatment, or disposal.
(c) A[n] owner/operator of a treatment, storage or disposal facility may store such wastes beyond one year; however, the owner/operator bears the burden of proving that such storage was solely for the purpose of accumulation of such quantities of hazardous waste as are necessary to facilitate proper recovery, treatment, or disposal.

Id. § 268.50(b), (c); see also HWTC III, 886 F.2d at 366-68 (upholding the 40 C.F.R. § 268.50(b) presumption that storage for less than one year is for permissible purposes).

As part of its November 22,1989, proposed rule establishing disposal and treatment standards for certain wastes, known as “Third Third” wastes because they fell into the last of three groups of wastes to be *330 regulated under the LDR program, the EPA sought comments on its existing approach and possible alternatives for implementing section 3004(j). See Land Disposal Restrictions for Third Scheduled Wastes, 54 Fed. Reg. 45,372, 48,496 (1989).

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Bluebook (online)
996 F.2d 326, 302 U.S. App. D.C. 60, 23 Envtl. L. Rep. (Envtl. Law Inst.) 21006, 36 ERC (BNA) 1913, 1993 U.S. App. LEXIS 14493, Counsel Stack Legal Research, https://law.counselstack.com/opinion/edison-electric-institute-v-us-environmental-protection-agency-cadc-1993.