LAWRENCE K. KARLTON, Senior District Judge.
Pending before the court is resolution of the trial of this case. As the court has stated at various times during the course of trial, both the facts and the law are difficult.
Nonetheless, to begin with the obvious, the court adopts the undisputed facts contained in the pretrial order.
The court is faced with a trial which the parties have tendered as one requiring resolution of contested expert opinion testimony. The experts who have testified are well qualified and appear to be reasonable people, who have come to contradictory results. The court wishes to be clear as to its opinion that this is not a case involving hired guns who will say anything someone pays them to say.
The testimony of the experts are not opinions in fields of exact science, but rather applied science. That fact helps account for at least some of the divergent opinions that have been received by the court. The reason for those divergent opinions, however, lies not only in the nature of the field but also in human nature.
Central to some of the experts' testimony is the application of various formulas, which in turn are dependent upon assumptions which provide the integers to be resolved by the equations employed. In that regard, the "reasonable" assumptions employed by the expert, may, however innocently, be influenced by the trial needs of the expert's sponsor.
Moreover, and perhaps more to the point, the applied science being contested was developed for purposes quite distinct from the questions asked in trial. In the real world, the applied science at issue seeks to determine where cleanups are necessary and how to proceed with the cleanup. In that regard, a defense expert, in essence, agreed with the court when asked whether the use of inexact, but experience-based, assumptions was sufficient for the purpose of cleanup. Such applications, however, may not be sufficient to carry the burden of proof at trial, since quite different questions are being asked. That is true even though that burden is no more than the preponderance of the evidence.
Nonetheless, the court is able to make a sufficient number of ultimate factual determinations.
The court concludes as follows:
1) PCE is listed as a hazardous substance under the act. 42 U.S.C. § 9601(14), 40 C.F.R. § 302.4.
2) The plaintiff's claims relative to the spill of DNAPL PCE are supported by the evidence.
3) The defendant's assertion that, by virtue of leaks in the waste water system used by plaintiff, the plaintiff spilled waste water into the vadose zone, is supported by the evidence.
4) During defendants' operation on the property the waste water system also leaked. Moreover, defendant engaged in both dry cleaning and the laundering of contaminated shop towels and other such items which contained PCE. Both of these activities contributed to PCE being deposited in the soil.
5) At various times after plaintiff acquired the property, plaintiff added washing machines which increased the volume of waste water being leaked.
6) Although plaintiff did not engage in dry cleaning, for some period of time it also laundered PCE-laden shop towels and like items. After the danger of PCE became apparent, plaintiff refused to launder items which were thought to contain PCE, and, accordingly, thereafter the amount of PCE in the waste water was reduced.
7) The waste water flow of both plaintiff and defendant touching the DNAPL carried the PCE to the ground water.
8) Vapor emanating from the deposited DNAPL PCE also contributed to the PCE in the ground water.
9) The contaminated ground water eventually reached property down stream, which caused the relevant governmental agencies to order plaintiff to undertake the cleanup of the site.
10) The evidence does not permit a rational allocation of fault between plaintiff and defendant.
The suit tests liability under CERLA. I now briefly sketch the court's understanding of the pertinent provisions of that statute.
Under CERCLA section 107(a), 42 U.S.C. § 9607(a), the federal government, state governments, and private parties may all initiate cleanup of toxic areas, and each such entity may sue potentially responsible parties for reimbursement of response costs.
Absent from the four elements of a prima facie case is any requirement that the plaintiff be innocent with regard to the contamination at issue.
With regard to allocating responsibility among potentially responsible parties, CERCLA provides overlapping and somewhat convoluted mechanisms. Section 107 imposes strict liability on potentially responsible parties.
It is clear that plaintiff has established defendant's liability under § 107. Simply put, the site is a facility within the meaning of the statute, there were releases from that facility, the releases caused plaintiff to incur response costs consistent with the national contingency plan, and the defendant is responsible for the release of DNAPL PCE and for its discharge of waste water, which, together with the plaintiff's waste water, mobilized the DNAPL and resulted in contamination of the ground water. Moreover, as noted above, vapor transport also affected the ground water. Given that the court concluded above that defendant cannot "establish[] a fixed amount of damage for which [it is] liable,"
Stipulation, ECF No. 861.
It is also undisputed that Ameripride received $500,000 in settlement from Chromalloy and $2,750,000 from Petrolane.
There is no question that items 1 and 2 are sums subject to equitable apportionment. Defendant, however, contests whether it should be considered responsible for any of the sums paid in settlement of the claims of Huhtamaki and Cal-Water. It asserts that it can only be responsible for "response costs," and since it cannot be said that those sums are exclusively response sums, plaintiff's claim must fail. For reasons explained in the court's summary judgment order, plaintiff cannot recover for those settlement payments under § 107.
Whether the settled claims were under the federal statute or pled as state claims, the gravamen of all those claims was the contamination of the ground water, the very claims at issue in the suit under CERCLA. The parties have not supplied the court with any authority addressing the question of how the court should account for AmeriPride's settlement with Cal-Am Water Co. and Huhtamaki, when that settlement involved multiple claims, nor, surprisingly, has the court's own research found any established guidance thereon.
While CERCLA § 9613 has provisions addressing contributions after settlement with a governmental party, there is no proviso directly dealing with settlements with nongovernmental parties.
Because the very purpose of § 113 is to do equity, such a purpose is clearly served by recognizing payments made to private claimants in settlement of state claims arising out of CERLA-focused suits. Accordingly, the court finds that the total amount subject to equitable apportionment is $18,295,651.00, less $3,250,000 for a total of $15,045,651.00. After including the consultant and other costs of $446,656.84 paid for investigation and remediation at the AmeriPride site since August 2010, and the $16,604.52 paid for regulatory oversight of the AmeriPride site since January 2011, the total amount subject to equitable apportionment is $15,508,912.36.
Section 223(f) gives the trial court broad discretion to consider whatever equitable factors it deems appropriate under the circumstances of the case. 42 U.S.C. § 9613(f)(1) ("In resolving contribution claims, the court may allocate response costs among liable parties using such equitable factors as the court determines are appropriate.")
The "Gore factors" are as follows: (I) The ability of the parties to demonstrate that their contribution to a discharge, release or disposal of a hazardous waste can be distinguished; (ii) The amount of the hazardous waste involved; (iii) The degree of toxicity of the hazardous waste involved; (iv) The degree of involvement by the parties in the generation, transportation, treatment, storage, or disposal of the hazardous waste; (v) The degree of care exercised by the parties with respect to the hazardous waste concerned, taking into account the characteristics of such waste; and (vi) The degree of cooperation by the parties with Federal, State, or local officials to prevent any harm to the public health or the environment.
Another district court when applying the Gore Factors added "critical factors" for courts to take into account in making CERCLA contribution allocations, to wit: the financial resources of the liable parties; the extent of the benefit that the parties received from the hazardous waste disposal practices; the extent of the parties' knowledge and awareness of the environmental contamination of the site; and the efforts made, if any, to prevent environmental harm and the efforts made to settle the case.
Yet another district court has further considered: (1) economic benefits received by a party as a result of its cleanup actions; (2) a party's efforts to conduct source control at its facility; (3) windfalls from settlements a party made with other PRPs; and (4) a party's decision to release some PRPs from liability.
None of these lists is intended to be exhaustive or exclusive, and "in any given case, a court may consider several factors, a few factors, or only one determining factor . . . depending on the totality of the circumstances presented to the court."
It is this court's view that, in many ways, the factors noted above will not fairly measure apportionment. First, it is hardly insignificant that, until the decision of the Delaware Supreme Court, the defendants were defunct corporations who had no capacity to respond to cleanup orders. Second, as noted above, the is no way of clearly allocating responsibility for the contamination of either the vadose zone or the ground water. The best view of the evidence is that, but for the DNAPL PCE deposits of the defendant, the ground water would not have been affected; however, it appears equally true that, but for the leaks in waste water system, the ground water might well not have been effected.
Given the facts as the court has found them, it concludes that the fairest apportionment is to divide responsibility equally. This would result in each party being responsible for $7,754,456.18 in costs expended so far. This number, however, fails to recognize that plaintiff has borne all of these costs for the many years since the first cleanup order. To roughly address this fact, the court will order defendant to also pay interest in amounts calculated in accordance with 42 U.S.C. § 9607 (incorporating the interest rate calculation provided in 26 U.S.C. § 9507(d)(3)(C)).
Accordingly the court order as follows:
2) The parties SHALL file a stipulation with the court within fourteen (14) days of the issuance of this order as to the interest payable by defendant by virtue of plaintiff's past expended costs, for which Defendant shall be liable.
3) Defendant SHALL be responsible for one half of all future cleanup costs.