United States v. Distler

803 F. Supp. 46, 1992 WL 274323
CourtDistrict Court, W.D. Kentucky
DecidedAugust 11, 1992
Docket88-0200-L(J), 88-0201-L(J)
StatusPublished
Cited by6 cases

This text of 803 F. Supp. 46 (United States v. Distler) is published on Counsel Stack Legal Research, covering District Court, W.D. Kentucky primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
United States v. Distler, 803 F. Supp. 46, 1992 WL 274323 (W.D. Ky. 1992).

Opinion

*49 JOHNSTONE, District Judge.

MEMORANDUM

This is a consolidated action for the recovery of environmental cleanup and response costs under 42 U.S.C. § 9601 et seq. (CERCLA) The case arises from the cleanup of two unpermitted hazardous waste drum disposal sites in Kentucky operated by Donald Distler and his company, Kentucky Liquid Recycling, Inc. Presently before the court are motions for summary judgment by numerous third party defendants. For the reasons set forth below, the motions will be denied.

FACTS:

In August of 1976, Donald Distler formed Kentucky Liquid Recycling, Inc. (KLR). KLR was to be in the business of recycling and disposing of industrial waste materials. Distler intended to collect industrial waste from various sources, filter and sell that portion of the waste that could be used as low grade fuel, and incinerate the non-useable remainder.

Unfortunately, Distler had no facilities for the incineration or disposal of waste. However, KLR proceeded- to enter into agreements to receive and haul large volumes of waste from several generators and waste brokers. This created an immediate and continuing disposal problem.

In September of 1976, KLR leased 5000 square feet of warehouse space on Rowan Street in Louisville, Kentucky (Rowan Street) and began to store drums of waste at this location. This drew the attention of the Louisville Fire Department, who felt uneasy about hundreds of drums of toxic, flammable waste stacked nine high in a residential district. By the end of December, 1976, the city informed Distler that the drums at Rowan Street would have to go. Removal of these drums occurred slowly over the following months.

Meanwhile, KLR purchased an old Standard Oil tank farm facility in New Albany, Indiana. The facility had a large basin into which any liquid could be dumped and then filtered and pumped into overhead storage tanks. KLR used this facility to store and process at least some of the waste it was collecting. In addition to the storage and processing of waste, Distler intended to construct an incinerator at this New Albany location. However, New Albany officials refused to grant a permit for the incinerator’s construction.

Storage capacity at New Albany was limited and the waste kept rolling in. The problem was compounded by mounting pressure from the Louisville authorities to empty Rowan Street. In March of 1977, KLR leased an old brickyard near West Point, Kentucky (the Brickyard) and immediately began to ship and dispose of waste at this location. KLR apparently kept no records of these waste shipments to the Brickyard.

At the end of March, 1977, an anonymous complaint was made to Public Health Officials that spills from drums of waste were entering the Ohio River. Two locations were identified; the Brickyard and a farm owned by Distler’s parents (the Farm). The Farm is a 13.68 acre tract of land on Dixie Highway in Louisville. Investigations began into these locations by state and federal authorities.

In mid-April 1977, U.S. EPA representatives, in conjunction with the Kentucky Department of Natural Resources and Environmental Protection, the FBI, and the Kentucky State Police, conducted sampling investigations of the Brickyard and Farm. At that time numerous drums of waste were observed at both locations and the presence of buried drums was detected at the Farm. Based upon information gathered during these- investigations,. restraining orders were issued by the Franklin Circuit Court prohibiting Distler from storing and/or disposing of industrial waste at the Brickyard or Farm sites. Evidence shows that these orders were violated by Distler.

In January of 1979, the EPA conducted a cleanup of the Farm and removed the drums located above the ground. In March 1984, the EPA went beck to the Farm site and removed the drums and containers which had been buried. From February 28, 1982 to March 26, 1982 the EPA removed *50 drums from the Brickyard. Some of the drums were traceable to specific waste generators. Many were unmarked or unidentifiable.

The United States filed suit in March of 1988 against Distler and eighteen original generator defendants seeking recovery under CERCLA of response costs incurred by EPA in cleanup of the Farm site. A separate action was filed against Distler and fifteen generator defendants relating to the Brickyard site. The Commonwealth of Kéntucky, Natural Resources and Environmental Protection Cabinet subsequently intervened to recover its response costs.

Thirteen of the eighteen defendant corporations filed complaints against 40 separate corporate third party defendants. The complaint in the Farm site action named 35 corporate defendants. The Brickyard complaint named 39 corporate defendants. The U.S. has recently amended its complaint to add 4 of the third party defendants as primary defendants in the Brickyard action. Thirty-four third party defendants have filed motions for summary judgment which are currently pending before the court. Ruling on nineteen of those motions will be reserved at the request of the parties while settlement negotiations continue.

THE LAW:

CERCLA was enacted in 1980 as a comprehensive response to the problems of hazardous waste. Section 107(a) of CERCLA imposes liability for response costs incurred by the government or private parties for cleanup of damages to natural resources on, inter alia, “generators” of hazardous wastes. A generator of hazardous waste is defined as:

any person who by contract, agreement or otherwise arranged for disposal or treatment, or arranged with a transporter for transport for disposal or treatment, of hazardous substances owned or possessed by such person, by any other party or entity, at any facility or incineration vessel owned or operated by another party or entity and containing such hazardous substances.

42 U.S.C. § 9607(a)(3). Each of the third party defendants in these actions are “generators” under the statutory definition.

CERCLA § 107 requires only a minimal causal nexus between the defendant’s hazardous waste and the harm caused by the release at a particular disposal site. Under this scheme, traditional tort notions such as proximate cause, do not apply. CERCLA only requires that the plaintiff prove by a preponderance of the evidence that the defendant deposited his hazardous waste at the site and that the hazardous substances contained in the defendant’s waste are also found at the site. Violet v. Picillo, 648 F.Supp. 1283 (D.R.I.1986) (citing United States v. Wade, 577 F.Supp. 1326 (E.D.Pa.1983)).

It is unnecessary under this standard of causation to trace the release of a hazardous waste to a particular generator to establish liability. For example, in United States v. Ottati & Goss, Inc., 630 F.Supp. 1361 (D.N.H.1985), the district court held certain generators liable for response costs based upon drums of waste deposited at the site, some of which had leaked their contents into the soil.

Free access — add to your briefcase to read the full text and ask questions with AI

Related

Cite This Page — Counsel Stack

Bluebook (online)
803 F. Supp. 46, 1992 WL 274323, Counsel Stack Legal Research, https://law.counselstack.com/opinion/united-states-v-distler-kywd-1992.