Spang & Co. v. Department of Environmental Resources

592 A.2d 815, 140 Pa. Commw. 306, 1991 Pa. Commw. LEXIS 324
CourtCommonwealth Court of Pennsylvania
DecidedJune 4, 1991
Docket918 C.D. 1990
StatusPublished
Cited by2 cases

This text of 592 A.2d 815 (Spang & Co. v. Department of Environmental Resources) is published on Counsel Stack Legal Research, covering Commonwealth Court of Pennsylvania primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Spang & Co. v. Department of Environmental Resources, 592 A.2d 815, 140 Pa. Commw. 306, 1991 Pa. Commw. LEXIS 324 (Pa. Ct. App. 1991).

Opinion

BYER, Judge.

Spang & Company (Spang) appeals from an order of the Environmental Hearing Board (EHB) sustaining the Department of Environmental Resources’ (DER’s) hazardous waste closure plan and post-closure bond for certain of Spang’s impoundments.

BACKGROUND

Spang owns and operates a manufacturing and research facility in East Butler, Pennsylvania. The facility consisted of a magnetics division and a manufacturing and tool division. Part of the manufacturing and tool division consisted *308 of the drill pipe plant, where drill pipe joints were manufactured and welded to pipes from 1977 through August 1985. 1

The drill pipe plant contained a copper electroplating line, which copper-plated the drill pipe and joints. Pipe to be copper-plated was first electropolished to remove any grease and machining material. After electropolishing, the pipe was cold water rinsed, acid etched and again rinsed with cold water. After the second rinsing, a solution of copper nuggets, copper cyanide, potassium cyanide, potassium hydroxide, and neochel (a rochelle salt) plated the pipe. After it was plated, the pipe was rinsed in water and a diluted plating solution. 2

This rinse water then was treated in treatment tanks with sodium hypochlorite or bleach, with the intent of destroying the free cyanide. Spang discharged the remaining liquid to an outside impoundment known as lagoon A. 3 Lagoon A’s effluent discharged into lagoon B. Lagoon B’s effluent discharged into nearby Bonnie Brook Creek. The sludge from the bottom of lagoons A and B was removed and stored in lagoon C. 4

DER’s regulations divide hazardous wastes into two categories: listed hazardous waste and characteristic hazardous waste. 25 Pa.Code § 261. A solid waste is a listed hazardous waste if it is within one of the listing descriptions found in 25 Pa.Code § 261.3, which incorporates the United States Environmental Protection Agency (EPA) list of hazardous wastes found at 40 C.F.R. Part 261, Subpart D. A listed waste is deemed hazardous unless it is specifically excluded by DER and EPA pursuant to a delisting petition. 5

*309 One of the listed hazardous wastes in the EPA list is “F006,” which is described as “Wastewater treatment sludges from electroplating operations.” The principal hazardous component of F006 is cyanide.

On March 7,1984, Spang submitted to DER a Notification of Hazardous Waste Activity, 6 indicating that Spang’s treatment process generated F006 hazardous waste. Spang also submitted a hazardous waste permit application indicating that it generated 13,944 gallons of F006 hazardous waste annually from its treatment tank and lagoons. By letter dated April 3, 1984, DER notified Spang that in its opinion Spang would need to either: (1) remove the sludge which accumulated in the bottom of the treatment tanks before it reached the lagoons; (2) secure a permit to operate the lagoons as a hazardous waste facility; (3) submit a delisting petition to the EPA; or (4) close the lagoons.

In April 1984, Spang modified its treatment system by following DER’s suggestion to remove the sludge which accumulated on the bottom of the treatment tanks before it reached the lagoons. Spang altered the treatment tanks so that the treated rinse water was discharged from pipes located nine inches above the bottom of the treatment tanks. This allowed the sludge to settle in the treatment tanks before the remaining rinsewater was discharged to the lagoons. After this modification, the sludge in the treatment tank was placed in drums and disposed off-site by a licensed transporter and disposer of hazardous waste. Spang identified these shipments as “Hazardous Waste Class F006.”

After implementing this modification, Spang also submitted a delisting petition to the EPA for the rinse water discharged through the treatment tanks’ pipes. Spang eventually abandoned the delisting petition when EPA noti *310 fied it . that the nickel content, although not hazardous, was too high to permit delisting.

On August 20, 1985, Spang submitted to DER its first closure plan for the lagoons, because it had commenced sending all processed wastewater to a treatment facility instead of discharging it into the lagoons. DER found Spang’s closure plan inadequate and substituted its own hazardous waste closure plan. 7

Spang appealed DER’s order to the EHB. Spang alleged that because all sludge generated after April 1984 was removed from the site, DER must establish that the rinse water and sludge Spang discharged into the lagoons before April 1984 was hazardous in order to apply the stringent hazardous waste closure requirements. Spang contended that all pre-April 1984 discharges were non-hazardous. 8

In March 1989, the EHB conducted a three-day hearing. 9 At the hearing, DER did not establish by physical evidence that concentrations of various materials in the lagoons met the criteria of hazardous waste (EHB finding of fact 30). Instead, DER relied on circumstantial evidence to show that hazardous wastes had been discharged into the lagoons prior to 1984.

DER’s circumstantial case was based upon: (1) regulations which provide presumptively that all types of electroplating create F006 hazardous waste; (2) numerous Spang documents which admitted the presence of F006; 10 and (3) the history of the drill pipe plant treatment system. DER argued that because the drill pipe plant treatment system sludge which accumulated after April 1984 was disposed of *? as hazardous waste, the treatment water discharged to the lagoons prior to April 1984, from which the sludge was never collected and removed, must have contained hazardous waste.

DER’s theory required application of the “mixture rule.” Simply stated, the mixture rule provides that the mixture of a listed hazardous waste (such as F006) and a solid waste yields a mixture that is also considered a hazardous waste. 40 C.F.R. § 261.3(a)(2)(iv); 25 Pa.Code § 261.3(b)(2). 11

DER’s theory also was based upon the contention that the drill pipe plant was the only source of any hazardous substances entering the lagoons. Spang contends DER did not specifically disclose before the hearing that it would make this contention.

PETITION TO REOPEN THE RECORD

Before the EHB made its adjudication,

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Bluebook (online)
592 A.2d 815, 140 Pa. Commw. 306, 1991 Pa. Commw. LEXIS 324, Counsel Stack Legal Research, https://law.counselstack.com/opinion/spang-co-v-department-of-environmental-resources-pacommwct-1991.