East Bay Municipal Utility District v. United States Department of Commerce

948 F. Supp. 78, 27 Envtl. L. Rep. (Envtl. Law Inst.) 20643, 43 ERC (BNA) 1918, 1996 U.S. Dist. LEXIS 18461, 1996 WL 718193
CourtDistrict Court, District of Columbia
DecidedDecember 4, 1996
DocketCivil Action 93-1715 (GK)
StatusPublished
Cited by4 cases

This text of 948 F. Supp. 78 (East Bay Municipal Utility District v. United States Department of Commerce) is published on Counsel Stack Legal Research, covering District Court, District of Columbia primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

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East Bay Municipal Utility District v. United States Department of Commerce, 948 F. Supp. 78, 27 Envtl. L. Rep. (Envtl. Law Inst.) 20643, 43 ERC (BNA) 1918, 1996 U.S. Dist. LEXIS 18461, 1996 WL 718193 (D.D.C. 1996).

Opinion

MEMORANDUM OPINION

KESSLER, District Judge.

This matter is before the Court on the parties’ Renewed Cross-Motions for Summary Judgment. Plaintiff brings this action under the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA), 42 U.S.C. § 9601 et seq., by the East Bay Municipal Utility District (EB-MUD). EBMUD seeks recovery for certain remediation costs it has incurred and may incur in the future to clean up hazardous waste at the Penen Mine. Plaintiff alleges that the U.S. government is liable for these costs because of the involvement of various government agencies with the zinc mining activities at Penn Mine during, and directly after, World War II. By Order of September 14,1993 (Richey, J.), this case was bifurcated. Accordingly, the issues presented for review in this portion of the bifurcated proceedings relate solely to liability. The parties filed Cross-Motions for Summary Judgment on this issue in April 1994. Judge Richey held a hearing on the Motions in May 1994, but, on May 27, 1994, denied them without prejudice to renewal at trial. The case was reassigned to this Court on July 1, 1994. At a status hearing on September 2, 1994, the Court allowed the parties to renew their motions. At a further status hearing on May 3, 1996, both parties reiterated their positions that the case could be disposed of on the basis of summary judgment and urged the Court to give serious consideration to the pending motions despite the daunting record and the many factual (although not necessarily material) issues in dispute. Upon review of the Cross-Motions, the Oppositions thereto, the Replies, the numerous supplemental memoranda submitted by both parties, and the entire record herein, the Defendants’ Renewed Motion for Summary Judgment is hereby granted and Plaintiff’s Renewed Motion for Partial Summary Judgment is hereby denied.

I. The Comprehensive Environmental Response, Compensation and Liability Act (CERCLA)

The Comprehensive Environmental Response, Compensation and Liability Act (CERCLA), 42 U.S.C. § 9601 et seq., was signed into law in 1980. It was enacted to address the increasing environmental and health problems associated with inactive hazardous waste sites. CERCLA encourages private cleanup of such hazards by providing a cause of action for the recovery of costs incurred for responding to a “release” of hazardous substances at any “facility.” Id. § 9607. Under CERCLA a person who incurs cleanup costs is entitled to recover from anyone who qualifies as a “responsible person” under the statute. Id. The federal *80 government is deemed a “person” under CERCLA. Id. § 9601(21).

Responsible persons under CERCLA include: (1) the current “owner” or “operator” of the facility; (2) any person who “owned” or “operated” the facility at the time of “disposal of any hazardous substance”; (3) any person who “arranged for disposal or treatment” of hazardous substances at the facility; and (4) any person who accepts hazardous substances “for transport to disposal or treatment facilities, incineration vessels or sites.” Id. § 9607(a). Any of these responsible persons is strictly liable for costs incurred in responding to the release of a hazardous substance at the facility, subject only to the defenses set forth in the statute. 42 U.S.C. § 9607; Kelley v. EPA, 15 F.3d 1100, 1103 (D.C.Cir.1994), reh’g denied, 25 F.3d 1088 (D.C.Cir.1994), cert. denied sub nom., American Bankers Ass’n v. Kelley, — U.S. -, 115 S.Ct. 900, 130 L.Ed.2d 784 (1995). Once responsible parties are identified, the court has the authority to “allocate response costs among liable parties using such equitable factors as the court determines are appropriate.” Id. § 9613(f)(1).

II. Background

The record submitted in this case is voluminous and includes documents dating from the 1800’s. However, the parties were able to sufficiently narrow the relevant issues so that they could submit a joint statement of undisputed facts in conjunction with their Cross-Motions for Summary Judgment. 1 Every fact cited herein, unless otherwise noted, comes from that statement. Although there are a number of significant of facts in dispute, 2 3 the Court specifically finds that none of these factual disputes are material to the issues presented in the parties’ Cross-Motions for Summary Judgment, and, therefore, they need not be resolved in order to decide the Cross-Motions.

Plaintiff EBMUD is a municipal utility district located in Northern California. R.S. ¶ 1. The Penn Mine is a currently inactive zinc and copper mine located upstream of the Mokelumne River in Calaveras County, California, adjacent to the Comanche Reservoir. R.S. ¶ 3. Copper was discovered in the mine in approximately 1861. Mining began shortly thereafter and continued until 1867. A smelter built at the Penn Mine site in 1863 was dismantled after mining stopped in 1867. Penn Mine’s next period of operation lasted from approximately 1899 through 1919. During that time, another smelter was built on the site that operated continuously during those twenty years. The ore mined was primarily copper. Although some zinc ores were removed, they were not recovered and used at that time. Approximately 87% of all the ore ever produced from Penn Mine was produced by. 1919. When the mine was shut down in 1919, the on-site smelter was also shut down and dismantled. The mine was kept pumped out until 1926, when the pumps were removed and the mine was allowed to fill with water. Between 1919 and World War II, there were several intermittent but largely unsuccessful attempts at reestablishing mining operations, which produced approximately 2,200 tons of ore. R.S. ¶¶ 20-27. There were additional periods of operation during World War II, R.S. ¶ 27, and after the Korean War. R.S. ¶ 98. All mining ceased in or about 1953, and the mine was closed down. Plaintiffs Statement of Material Facts as to Which There Is No Genuine Issue, ¶ 7. 3

*81 Operations at Penn Mine left debris containing hazardous substances spread over 20 acres of significantly disturbed land at the site. R.S. ¶ 3. Some of this material was deposited as a result of mining conducted during World War II. These materials contain hazardous substances, including copper, zinc, cadmium and lead. When the waste rock, mine tailings, and excavated ores are exposed to oxygen and water, they oxidize and form acid. This acid leaches heavy metals in the area of the reaction. Rainwater or other water flowing over the oxidized materials readily dissolves and carries the acid and metals. This is commonly known as acid rock drainage or acid mine drainage. Two intermittent streams flow through the Penn Mine site carrying acid mine drainage.

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948 F. Supp. 78, 27 Envtl. L. Rep. (Envtl. Law Inst.) 20643, 43 ERC (BNA) 1918, 1996 U.S. Dist. LEXIS 18461, 1996 WL 718193, Counsel Stack Legal Research, https://law.counselstack.com/opinion/east-bay-municipal-utility-district-v-united-states-department-of-commerce-dcd-1996.