City and County of Denver v. Adolph Coors Co.

829 F. Supp. 340, 24 Envtl. L. Rep. (Envtl. Law Inst.) 20112, 1993 U.S. Dist. LEXIS 3582, 1993 WL 293878
District Court, D. Colorado·Decided February 24, 1993·No. Civ. A. 91-F-2233·Published·Cited by 15 cases

Opinion

ORDER REGARDING APPROVAL OF SETTLEMENTS: 1993-5

SHERMAN G. FINESILVER, Chief Judge.

This is a case involving environmental contamination at the Lowry Landfill Site (“Lowry” or “the Site”), operated at various times by Plaintiffs City and County of Denver (“Denver”), Waste Management of Colorado, Inc. (“WMC”), and Chemical Waste Management, Inc. (“CWM”). This matter comes before the Court on Plaintiffs’ Motion for Approval of Settlements, filed October 20, 1992. Jurisdiction is based upon 28 U.S.C.A. § 1331 and 42 U.S.C.A. §§ 9601 and 9607. The litigants have fully briefed the issues. For the reasons stated below, the motion is GRANTED in PART.

I. Background

Lowry, located 20 miles southeast of Denver, was listed on the CERCLA National Priorities List (“NPL”) on September 21, 1984, as a hazardous waste site. 49 Fed.Reg. 37,070 (1984). Plaintiffs, all current or former operators of Lowry, seek damages from numerous alleged generators and transporters of the hazardous waste under sections 107 and 113 of the Comprehensive Environmental Response, Compensation, and Liability Act (“CERCLA” or “Superfund”). 42 U.S.C.A. §§ 9601 et seq. (West 1983 & Supp. 1992). Plaintiff Denver also alleges certain common law causes of action.

The Lowry Landfill was owned and operated by the United States beginning in the early 1940s. On July 15, 1964, the United States conveyed the site to Denver by quitclaim deed with the condition that the site be used as a landfill at least until 1984. Denver operated the site from 1964 to 1980 as a regional industrial and municipal waste site.

On July 7, 1980, CWM executed a contract with Denver to operate the site and WMC operated the site from August 12, 1980 until August 3, 1990. Denver, CWM, and WMC *342 claim that they have incurred and will continue to incur response, cleanup, and remediation costs. Defendants are entities alleged to be either generators or transporters of hazardous wastes to Lowry. Most defendants have been identified by the Environmental Protection Agency (“EPA”) as potentially-responsible parties (“PRPs”) at the Lowry Landfill site pursuant to 42 U.S.C.A. § 9607(a) (West 1983 & Supp.1992).

Following years of failure by the Environmental Protection Agency (“the EPA”) to effectuate settlement with Lowry PRPs, Plaintiffs diligently worked out settlements with 119 PRPs totalling over 24 million dollars. In the motion before the Court, Plaintiffs have applied for an order (1) approving the settlements, (2) barring claims against the settlors for contribution or response costs, except as provided for in the settlement agreements (“the Agreements”), and (3) declaring that the nonsettlor’s share of liability is reduced by the amount paid by the settlors for their volumetric share of the remedial costs at the Site.

The settlements executed by Plaintiffs fall into three categories: de minimis, mid-tier, and one agreement with John Todd, Inc. based on the corporation’s inability to pay. A de minimis PRP had to meet the same four criteria as required in the EPA’s de minimis settlements: (1) the PRP’s § 104(e) response was adequate and complete; (2) the PRP’s volumetric contribution of waste was 300,000 gallons or less; (3) the PRP was not involved in any litigation against EPA concerning the Site; and (4) the PRP’s waste stream was not significantly more toxic or of greater hazardous effect than other waste streams at the Site. Defendants who failed to qualify for de minimis status were classified as either mid-tier or high-tier, depending upon their volumetric contribution.

Each of the settlements contained up to five key components. The first component is the estimated cost of the remedy. An estimated cost of the remedy was agreed to by the parties for purposes of negotiations and then reduced by 20 percent to account for Plaintiffs’ share of the remedial costs. The estimated cost of the remedy used in the de minimis agreements — $500 million — was greater than that for the mid-tier agreements — $310 million — because the mid-tier settlements anticipate a remedial cost reopener that potentially subjects mid-tier settlors to greater liability. All settlements were based on an estimated cost of the remedy greater than the estimate offered by the nonsettling defendants. Therefore, the settlors paid a greater amount — and the nonsettlors will be credited a greater amount— than if the nonsettlors’ estimate had been used.

The second and most important component represents the settlors’ volumetric contribution of waste containing hazardous substances at the Site. To determine a PRP’s volumetric contribution of waste to the Site, the parties relied on a thorough and continually updated EPA study entitled “Protocols for Identifying and Determining Volumetric Contribution for Lowry Landfill (§ 6).” Each settlor’s volumetric waste contribution taken as a percentage of all waste at Lowry was then multiplied by the total estimated cost of the remedy (less Plaintiffs’ 20 percent) to arrive at the settlor’s estimated share of the remedy.

The third component, for de minimis settlements only, is a cost overrun premium paid by settlors in addition to the payment for their volumetric share. The cost overrun premium allows parties to settle with finality their liability at the Site without regard to cost overruns. In exchange for bearing the risk of cost overruns, Plaintiffs are protected against unanticipated increases in the cost of the remedy based on regulatory and other changes, The mid-tier settlement equivalent of the third component, due to the larger payments involved, is a reopener clause that allows the parties to revisit the Agreements in the event the actual cost of remedy exceeds the estimated cost.

The fourth component of some settlements was for optional premiums the settlor could pay in consideration for Plaintiffs’ agreement to assume certain additional obligations, most of which are unrelated to response costs or other cleanup of the Site. The greater the assumed obligation premium a settlor was willing to pay, the more potential future obligations of the settlor Plaintiffs were willing *343 to assume. The optional assumed obligation premium was also offered to the settlors in order to afford greater finality in the liability associated with Site litigation. 1

The fifth and final component consists of two separate provisions regarding the parties’ attempts to address both the uncertainty of current information and the inability to pay of other PRPs. First, a standard “new information” reopener such as that used by the EPA is incorporated in all de minimis and mid-tier settlements. To protect Plaintiffs against the possibility that a settlor’s full waste contribution to the Site had not been discovered at the time or settlement, Plaintiffs may collect additional monies if new information comes to light indicating that a settlor contributed a greater volume of waste. Second, because CERCLA recognizes that a PRP may be jointly and severally liable, Plaintiffs’ settlements reflect a proportion of response costs attributable to bankrupt or financially insolvent PRPs. This portion is referred to as an “orphan share.” The de minimis

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

City and County of Denver v. Adolph Coors Co., 829 F. Supp. 340, 24 Envtl. L. Rep. (Envtl. Law Inst.) 20112, 1993 U.S. Dist. LEXIS 3582, 1993 WL 293878 (D. Colo. 1993).

829 F. Supp. 340 (City and County of Denver v. Adolph Coors Co.) — published by Counsel Stack Legal Research, free access to 12M+ legal documents.

Related

Coomer v. Lindell
D. Colorado, 2024
Gurley v. CITY OF WEST MEMPHIS, AR
489 F. Supp. 2d 876 (E.D. Arkansas, 2007)
American Cyanamid Co v. A. Capuano Brothers
381 F.3d 6 (First Circuit, 2004)
State of NY v. Solvent Chemical Co., Inc.
984 F. Supp. 160 (W.D. New York, 1997)
Stearns & Foster Bedding Co. v. Franklin Holding Corp.
947 F. Supp. 790 (D. New Jersey, 1996)
Town of New Windsor v. Tesa Tuck, Inc.
919 F. Supp. 662 (S.D. New York, 1996)
Barmet Aluminum Corp. v. Doug Brantley & Sons, Inc.
914 F. Supp. 159 (W.D. Kentucky, 1995)
Charter Township of Oshtemo v. American Cyanamid Co.
898 F. Supp. 506 (W.D. Michigan, 1995)
Ekotek Site PRP Committee v. Self
881 F. Supp. 1516 (D. Utah, 1995)
T H Agriculture & Nutrition Co. v. Aceto Chemical Co.
884 F. Supp. 357 (E.D. California, 1995)
Hillsborough County v. A & E Road Oiling Service, Inc.
853 F. Supp. 1402 (M.D. Florida, 1994)
Hillsborough County v. a & E Road Oiling Service
853 F. Supp. 1402 (M.D. Florida, 1994)
United States v. SCA Services of Indiana, Inc.
849 F. Supp. 1264 (N.D. Indiana, 1994)
Barton Solvents, Inc. v. Southwest Petro-Chem, Inc.
834 F. Supp. 342 (D. Kansas, 1993)