Full opinion text
OPINION PETTINE, Senior District Judge. The State of Rhode Island (“State”) seeks to hold the defendants jointly and severally liable for one million six hundred and thirteen thousand four hundred and thirty-seven dollars and thirty cents ($1,613,437.30) it expended in cleaning up a hazardous waste site in Coventry, Rhode Island known as the Picillo Pig Farm; it also asks this Court to declare that the defendants must respond in damages for all remedial costs it may incur in the future in the investigation and remediation of damages to the State’s natural resources allegedly resulting from the waste disposal by these defendants at said site. The action is brought pursuant to the Comprehensive Environmental Response Compensation and Liability Act of 1980 (“CERCLA”) as amended by the Superfund Amendments and Reauthorization Act of 1986 (“SARA”) 42 U.S.C. sections 9601-9675. The complaint originally named thirty-five defendants who were either owner/operators of the site, parties who allegedly transported waste there, parties alleged to have arranged for their waste to be transported to the site, and parties alleged to have produced waste deposited at the site. However, on the day designated for trial, the State and the United States Environmental Protection Agency (“EPA”), a non-party, settled with all the defendants except Olin Corporation (“Olin”), Hydron Laboratories, Inc. (“Hydron”), American Cyanamid Company (“American Cyanam-id”), Exxon Research and Engineering Company (“Exxon”), and Rohm & Haas Company (“Rohm & Haas”). The settlements totaled 5.8 million dollars and included various agreements to perform specific remedial action. The State has represented that it will receive 25 percent of the settlement with the remaining 75 percent going to the federal agency. These remaining defendants claim that the State has failed to prove that the materials in question were hazardous; they also argue that joint and several liability which the State seeks to impose is not appropriate in this case, and that they have the right to interpose several defenses, equitable and legal, which preclude recovery against them. For the reasons which follow, I find for the plaintiff. Prolixity is not a commendable hallmark of a legal opinion; the extent of the footnotes here indicate this paper deserves just such an unenviable stamp. In the margin I have substantially quoted from prior opinions rendered in this case; I do so because they set forth the dispositive law of vital legal issues and so I incorporate the same as part of this ruling. Colloquy took place throughout the trial as though certain of these issues had not been rendered; none of it was meaningful enough to cause me to change my position. I. FACTUAL BACKGROUND As an overall, with greater specificity being recited at appropriate points in the discussion of the legal issues, I repeat what I stated in my Opinion and Order of November 20, 1986, Violet v. Picillo, 648 F.Supp. 1283 (D.R.I.1986) ruling on Olin’s Motion for Summary Judgment: This case arises from the chemical catastrophe of the Picillo pig farm in Coventry, Rhode Island. State environmental authorities discovered this chemical wasteland in 1977 after combustible chemicals caused a dramatic explosion and towering flames to rip through the waste disposal site. After the fire, state investigators discovered large trenches and pits filled with free-flowing, multicolored, pungent liquid wastes; they also excavated approximately 10,000 barrels and containers in varying states of decay containing hazardous chemical wastes. Id. at 1286. In this case, the plaintiff claims the following materials found at the site were specifically traced to the defendants: 303 five-gallon cans and 49 fifty-five gallon drums to Rohm & Haas; 21 fifty-five gallon drums to Hydron; 15 fifty-five gallon drums to Exxon; 3 fifty-five gallon lab packs and 11 fifty-five gallon drums to Olin; and 10 fifty-five gallon drums to American Cyanamid. II. JURISDICTION In the pre-trial stages of this action, defendants Exxon and Hydron filed motions for dismissal pursuant to Fed.R.Civ.P. 12(b)(2) for lack of in personam jurisdiction. Each disavowed any knowledge of how waste allegedly generated by them came to rest at the Picillo site, and each claimed to lack any significant links to the state of Rhode Island independent of the present litigation. In Violet v. Picillo, 613 F.Supp. 1563 (1985), I set forth a lengthy and detailed discussion of the jurisdictional aspects of this case and I repeat the same here in the margin. I concluded by saying: I emphasize that only a prima facie showing of jurisdiction has been made here.... the final determination of the key fact issues bearing on jurisdiction over the person will be made at trial. If they are decided in a way that defeats jurisdiction as to [any] defendant, as to that defendant plaintiffs action will then be subject to dismissal for want of jurisdiction over the person. Id. at 1579 n. 17 (citing North American Video v. Leon, 480 F.Supp. 213, 216 (D.Mass.1979)). Hydron renews its motion post-trial, nourished by the testimony of David Rapa-port, a director and Vice President (legal); he testified that: Hydron was a Delaware corporation; Its principal place of business in 1977 was New Brunswick, New Jersey; It has never had any other principal place of business, or any other place of business; It never had an office in Rhode Island; To his knowledge, and based on a search of Hydron’s records, the only contact with the State of Rhode Island was the delivery in 1976, by mail, of a free sample of one ounce of a chemical to a Rhode Island firm which had requested that the sample be sent; Hydron did not sell or ship any other products into the State of Rhode Island; Hydron never qualified to do business in Rhode Island; It never nominated any agent for service of process in Rhode Island; It placed no ads in Rhode Island. In Violet, ruled that non-resident generators of hazardous wastes were akin to national distributors who placed their products into the stream of commerce through intermediaries. 613 F.Supp. at 1576. I held that because these generators “should have known, if [they] did not, in fact know, that it was dispatching its hazardous wastes into a stream of commerce broad enough to include any and all states” it did not offend due process to subject them to suit in one of the states comprising its “market.” Id. at 1576-77 (citations omitted). I am not diverted from my original holding by Hydron’s proffered evidence. The analysis of jurisdiction in Violet was premised upon a theory of specific jurisdiction. See id. at 1575 n. 12. A court exercises specific jurisdiction when the plaintiffs claims “arise out of” or are “directly related” to defendant’s contacts with the forum state. DuPont Tire Serv. v. North Stonington Auto-Truck Pl., Inc., 659 F.Supp. 861, 863 (D.R.I.1987) (J. Lagueaux). General jurisdiction, however, arises where plaintiff’s claims do not arise out of or are not directly related to defendant’s claims. Id. Consequently, my only concern in Violet was whether the shipment of hazardous wastes into Rhode Island through intermediaries was a sufficient “contact” with the state for purposes of jurisdiction. Because Hydron’s evidence relates to contacts unrelated to the cause of action, that is, contacts relevant to the concept of general jurisdiction, I see no reason to reconsider my earlier position. I am moved, however, to reconsider my opinion in Violet for another reason. The holding in that case was predicated on the “stream of commerce” doctrine seemingly sanctioned in World-Wide Volkswagen Corp. v. Woodson, 444 U.S. 286, 100 S.Ct. 559, 62 L.Ed.2d 490 (1980). There, the Supreme Court observed that “[t]he forum state does not exceed its powers under the Due Process Clause if it asserts personal jurisdiction over a corporation that delivers its products into the stream of commerce with the expectation that they will be purchased by consumers in the forum state.” Id. at 297-98, 100 S.Ct. at 567. While Violet was the first case to use this analysis in toxic waste cases, other courts confronted with the issue found it suitable as well. See e.g., Allied Towing v. Great Eastern Petroleum Corp., 642 F.Supp. 1339, 1355-56 (E.D.Va.1986); U.S. v. Conservation Chemical Co., 619 F.Supp. 162, 247-50 (W.D.Mo.1985). Since Violet and these other cases were decided, the Supreme Court and the First Circuit Court of Appeals handed down significant opinions concerning the continued vitality of the “stream of commerce” doctrine. While neither of these opinions were raised by the parties, they must be examined for their effect on the instant litigation. In Asahi Metal Ind. v. Super. Ct. of Cal., Solano Cty., — U.S. —, 107 S.Ct. 1026, 94 L.Ed.2d 92 (1987), Asahi Metal, a Japanese manufacturer of tire valves, sold its products to a Taiwanese tire manufacturer, who distributed its tires to the United States. A product liability suit was brought in California state court against the Taiwanese tire producer arising from a motorcycle accident allegedly caused by a defect in a tire. The Taiwanese company thereupon filed a cross-complaint against Asahi Metal, seeking indemnification. Asahi argued that it was not properly before the California courts. The California Supreme court disagreed. It held that Asahi’s intentional act of placing its valves into the stream of commerce by delivering them to the Taiwanese tire manufacturer, coupled with its awareness that some of them would end up in California, were sufficient contacts to support jurisdiction. The United States Supreme Court reversed. In a divided opinion, the plurality of four justices held: The placement of a product into the stream of commerce, without more, is not an act of the defendant purposefully directed to the forum state. Additional conduct of the defendant may indicate an intent or purpose to serve the market in the forum state, for example, designing the product for the market in a forum state, establishing channels for providing regular advice to customers in the forum state, or marketing the product through a distributor who has agreed to serve as the sales agent in the forum state. But a defendant’s awareness that the stream of commerce may or will sweep the product into the forum state does not convert the mere act of placing the product into the stream into an act purposefully directed toward the forum state. Id. at 1033. Although the plurality’s renunciation of a doctrine that had acquired a substantial pedigree among the lower federal courts was soundly criticized by five justices in two concurring opinions, it must be considered the last word on this aspect of minimum contacts doctrine. See Dupont Tire Service Center, Inc., supra, 659 F.Supp. at 863. The First Circuit also had occasion to discuss the “stream of commerce” doctrine in Dalmau Rodriguez v. Hughes Aircraft Co., 781 F.2d 9 (1st Cir.1986). In that case, Hughes Aircraft company, a Delaware corporation with offices in California, manufactured helicopters which it sold to an intermediary who had a contract to supply helicopters to the Puerto Rico police department. An alleged defect in the helicopters injured two police officers, who brought suit against Hughes. While Hughes argued lack of minimum contacts, plaintiffs argued that because Hughes knew that its helicopters were to be delivered to Puerto Rico, stream of commerce doctrine permitted jurisdiction. The first circuit, however, rejected this argument: Assuming that Hughes knew that the destination of the helicopters was Puerto Rico, we do not think that the sale of two helicopters to a police department can be the source of a stream of commerce. This is not like opening up a particular territory for sales to the general public.... There is nothing in the record showing that Hughes advertised regularly in magazines circulated in Puerto Rico or aimed its advertising at Puerto Rico. We do not think that whether Hughes knew that the helicopters were being sold to Puerto Rico police department has any jurisdictional significance. The test is not knowledge of the ultimate destination of the product, but whether the manufacturer has purposely engaged in forum activities so it can reasonably expect to be haled into court there.... Id. at 15. I believe that the extra conduct seemingly required by the Asahi and Rodriguez courts is not necessarily required in cases of the kind presented here. It has long been acknowledged, and it was unanimously reaffirmed by the Court in Asahi, that “the determination of the reasonableness of the exercise of jurisdiction in each case” will depend, not only on an evaluation of the defendant’s connection with the forum state, but also on an evaluation of “the interests of the forum state, and the plaintiffs interest in obtaining relief.” 107 S.Ct. at 1033-34 (section joined by unanimous Court). As the first circuit has stated, “[p]art of the due process equation involved in the minimum contacts standard is whether a defendant’s activities relating to a particular state are such as to give that state a legitimate interest in holding a defendant answerable on a claim related to those activities.” Johnson Creative Arts, Inc. v. Wool Masters, Inc., 743 F.2d 947, 951 (1st Cir.1984). It is apparent from this, and it has generally been recognized, that the nature and significance of the state’s interest may have a bearing on the nature and extent of the necessary contacts. See Hanson v. Denckla, 357 U.S. 235, 252, 78 S.Ct. 1228, 1239, 2 L.Ed.2d 1283 (1958); see also Chattanooga Corp. v. Klinger, 528 F.Supp. 372, 378 (S.D.Tenn.1981) (in applying the minimum contacts test the requisite amount of contacts should vary according to the state’s interest); Comment, Federalism, Due Process, and Minimum Contacts: World-Wide Volkswagen Corp. v. Woodson, 80 Colum.L.Rev. 1341, 1351-52 (1980). As I stated in Violet: Certainly Rhode Island’s interest in adjudicating this suit could hardly be more compelling. In addition to the state’s recognized “significant interest in redressing injuries that actually occur within the State,” Rhode Island has an extraordinarily strong sovereign interest in providing a forum for actions concerning injury to land within its borders, and for actions which seek recovery of public monies expended to protect such land. 613 F.Supp. at 1579 (citations omitted). Enhancing this interest is the fact that we are not here dealing with an ordinary product. The defendants dispatched volatile and inherently dangerous toxic substances. “Injuries caused by inherently dangerous articles imported through independent distributors certainly fall within that class of litigation with which the forum state has a deep interest in adjudicating.” Poyner v. Erma Werke GMBH, 618 F.2d 1186, 1192 (6th Cir.), cert. denied, 449 U.S. 841, 101 S.Ct. 121, 66 L.Ed.2d 49 (1980); see Klinger, supra, 528 F.Supp. at 378 (“contacts may be minimized if the claim involves the placing of a dangerous instrumentality in commerce”); see also Asahi Metal Ind., 107 S.Ct. at 1038 (Stevens, J., White, J., and Blackmun, J., concurring) (“Whether or not ... conduct rises to the level of purposeful availment requires a constitutional determination that is affected by the volume, the value, and the hazardous character of the components.”) (emphasis added). Additionally, the fact that the non-resident generators operate in a nationally regulated industry increases the significance of the contact with the forum. As one court has put it, “under CERCLA, a generator-defendant can reasonably anticipate being haled into court in any state in which [its] hazardous substances ... are found.” U.S. v. Conservation Chemical Co., 619 F.Supp. 162, 249 (D.Mo.1985); see also Allied Towing Corp. v. Great Eastern Petroleum Corp., 642 F.Supp. 1339, 1356 (E.D.Va.1986) (“the scope of ‘foreseeability’ broadens when the enterprise giving rise to the action is subject to pervasive federal regulation”). Moreover, simply as a matter of elemental fairness, it is not unreasonable to expect a person engaged in a highly regulated activity “to suffer the consequences of being sued in a distant place.” Oxford First Corp. v. PNC Liquidating Corp., 372 F.Supp. 191, 202 (E.D.Pa.1974). As the Supreme Court has recognized: [WJhen an entrepreneur embarks upon [certain types of] business activities, he has voluntarily chosen to subject himself to a full arsenal of governmental regulation. ... [Bjusinessmen engaged in such federally licensed and regulated enterprises accept the burdens as well as the benefits of their trade.... The businessman in a regulated industry in effect consents to the restrictions placed upon him. Marshall v. Barlow’s, Inc., 436 U.S. 307, 314, 98 S.Ct. 1816, 1821, 56 L.Ed.2d 305 (1978). Finally, as I stated in Violet, the interests of the plaintiff state government “in obtaining convenient and effective relief,” World-Wide Volkswagen, supra, 444 U.S. at 292, 100 S.Ct. at 564, fairly depends upon its ability to litigate this action in a single forum. In such multiparty, potentially labrynthine litigation, it will no doubt substantially burden the state to force it to proceed in parallel or piecemeal actions — and doubly so in light of the limited litigation resources available to the state. 613 F.Supp. at 1579. Accordingly, I find that this court has the requisite jurisdiction. III. LIABILITY I discussed generator liability at length in Violet, 648 F.Supp. at 1288-90; I now incorporate that discussion as part of this ruling. Rohm & Haas Company It is clear that this major chemical company took every precaution in the disposal of its wastes; it was separated into categories, packed into 58 gallon metal, open-head drums (“lab packs”) cushioned with vermiculite and absorbent materials, and disposed of through a licensed transporter. During 1976-1977, the pertinent period here, it contracted with Jonas Waste Removal (“Jonas”), to transport its waste exclusively to licensed disposal sites in Pennsylvania and New Jersey with directions stating, “[disposal of these waste materials is not to be in violation of an ordinance, regulation or law of responsibility for safe delivery and disposal of the material after leaving (the premises).” And as the defendant states, it is uncontra-dicted that at no time was any material consigned to Rhode Island. However, during this period approximately 4,800 fifty-five gallon lab packs were consigned to Jonas and the state claims 303 five-gallon drums of this total were found at the Picil-lo site; the defendant argues that this is an uncorroborated statement nowhere to be found in the record. The fact remains that this defendant agreed to have its materials removed. The record shows it “paid the State’s contractor approximately $32,000 as the costs for handling the removal of Rohm & Haas materials.” Certainly this is an indication of the quantity of waste removed. The removal and identification of this material was with the assistance of a Mr. Joseph Pawlikowski of Rohm & Haas, who was the superior responsible for that company’s waste disposal. In mitigation, the defendants point out that 20 drums, which were segregated in one area, were intact without any observable leakage. However, this was disputed by John Leo, an employee of the State Department of Environmental Management. The defendant also points to Mr. Leo’s testimony that Rohm & Haas, “removed all of their toxic waste that could be removed.” The defendant did not go far enough because Mr. Leo also stated, in answer to a question as to what was left, “[wjhich left the contaminated soil from the broken bottles that had leaked out into the pit from their lab packs.' That, of course, was lost in the environment which would have added to the contamination in the groundwater.” He further said that he personally saw removed from the pit “at least four or five drums” containing liquid which was spilled because the drum heads were crushed and had holes on the side caused by the bulldozer. “They were eventually shown to be Rohm & Haas material ... [t]hose drums were Rohm & Haas drums.” One of the drums contained allyl alcohol, which is a flammable, extremely poisonous material; “[T]hey [representatives from Rohm & Haas] were shown the barrel that contained nothing but this allyl alcohol ... this material is extremely poisonous ... a class B poison and by DOT regulations as class B poison is extremely dangerous material.” The material spilled into the ground was removed as contaminated soil. Mr. Leo could not state what quantum of soil was contaminated by this defendant; though he did know the total amount of soil removed; but, “[h]ow much is actually responsible from Rohm & Haas or whatever other companies are involved I can’t tell you. I mean we didn’t proportion out the soil.” I accept the State’s estimate as to the quantum of material found at the dump and that it was toxic hazardous waste. Accordingly, this defendant is liable to the state as set forth, infra. Exxon Research and Engineering Company The State contends that 15 Exxon drums were excavated; Mr. Leo so testified; however, he also acknowledged that the number was based on his recollection and not his records, which identified only one Exxon “lab pack”; this single drum was rusted and dented without any evidence of spillage. When pressed for records corroborating his testimony of 15 drums, he stated, “I cannot point to any one record. It’s made up of film, photographs, my own visible ... seeing barrels at the site, and everything else. No record was made ... I was asked by the Attorney General’s office to put together an estimation of the number of barrels found. That’s what I did, and that was based on my records, the amount of material, my own recollection as being there on site for the number of barrels that were there.” The culmination of his testimony was the acknowledgement that there were no corroborating records; the number 15 was based on his best recollection. The defendant developed, as it states in its Memorandum at 32, that “[i]ndeed, during his [Leo’s] deposition in March 1985, Mr. Leo himself testified that he saw only one drum ... the contents of which were identifiable to Exxon.” Another witness, Alan Brodd, testified for the State. He was the site supervisor who was on the site on a daily basis during the excavation in question. He had “overall responsibility for the site safety and the day-to-day operation and activities at the site.” His duties required him to sample, analyze, and interpret results of such samplings and make judgments as to whether or not the materials were hazardous. He testified he saw twenty or thirty half pint or pint bottles that bore Exxon labels. The State’s reply to the foregoing is: “Although Mr. Brodd saw only one lab pack attributable to Exxon ... Mr. Brodd’s managerial position did not permit him to have the type of direct, regular involvement in the excavation activities over which John Leo had primary responsibility.” Plaintiff’s Reply Memorandum at 18. Exxon utilized the services of a transporter licensed by the State of New Jersey and the Federal Government; in addition, Exxon personnel visited the disposal sites of its transporters to be assured of their adequacy. At one of the sites the transporter insured that the wastes were removed from their lab packs and incinerated; at this same site, procedures were employed to verify receipt of all the waste to be disposed of and incinerated. Exxon never deliberately sent any of its material to the Picillo site nor did it ever utilize any of the transporters who used the site. I find Exxon employed every precaution to prevent the illegal and/or improper disposal of its waste. Nevertheless, I must also find that twenty or thirty bottles, as described supra, were found at the site. However, although, there was testimony at trial that the Exxon materials were “probably flammable,” no further proof of toxicity was offered. Accordingly, I find that the State has not met its burden of proving the material allegedly found by Brodd was hazardous within the meaning of CERCLA. Judgment must be entered for this defendant. American Cyanamid Mr. Leo testified that he believed or recalled that, “there were ten drums from American Cyanamid based on going through the records and personally being there and seeing the drums.” He copied the data recorded on the labels of containers found at the site and contacted Dr. Ralph Wainwright, supervisor of waste disposal at American Cyanamid, who, using the code numbers found on the labels, identified the material as coming from their Agricultural Division, which “makes poisons and pesticides in New Jersey.” Mr. Leo then talked to a Dr. Luke of American Cyanamid and, based upon that conversation and conversations with Dr. Wainwright, testified that, “based on what I had — based on the code numbers that I was giving them the material was poison ‘B’, again, very toxic material [such as] experimental pesticides and toxins used in ... veterinarian supplies for worms and so forth and cows and pigs and that the other material was a catalytic resin.” A partial record was made of the day and date of these phone calls as well as of the code numbers. These records were made available to the defendants. The plaintiff does not dispute the following facts: During 1977, Ralph Wainwright was supervisor of industrial hygiene and safety at American Cyanamid and was responsible for disposal of wastes generated at its laboratory. All wastes were labeled with code names and generic descriptions. Wastes were sorted into categories at each laboratory and a form prepared accurately describing each waste and the container in which it was placed. Mr. Wainwright reviewed copies of these forms to assure that they were completed and the waste properly described. Once he was satisfied, the materials were collected and brought to a storage area where they were packed into 55 gallon steel drums to form lab packs, using vermiculite as an absorbent material. Each drum contained sheets showing precisely what materials were packed therein. Each drum contained compatible materials, e.g. flammables, liquids, solids, poisons, corrosives, etc. Each drum was labeled on the outside with information relating to the company and location, a bright symbol and writing to indicate the type of hazardous material, and the number of the drum. In sum, every effort was made to properly label and identify these drums and their contents. The drums were then manifested and picked up by a transporter. During the period 1970-1977, American Cyanamid used one transporter extensively for lab pack material, Chemical Control Corporation of Elizabeth, New Jersey, and two others on certain occasions (water-reactive wastes and PCBs were handled specially). Pursuant to company policy, Mr. Wainwright visited the Chemical Control facility to make sure that wastes were handled properly. He visited the site on three occasions between 1972 and 1977. Lab packs were to be incinerated. He inspected the incinerator. He inspected the licenses. He was satisfied that the facility was a proper one for the disposal of American Cyanamid wastes. The state does not take issue with American Cyanamid’s claimed diligence in the selection of its transporter. Nor, in fact, do I. Unfortunately for American Cyanamid, however, this line of argument gets it nowhere. As I ruled in Violet, 648 F.Supp. at 1290-93, and as I reaffirm infra, the strict liability scheme of CERCLA imposes liability upon generators even though they may have taken precautions in selecting what appeared to be a responsible transporter. Moreover, as a purely factual matter, it is not at all clear that American Cyanamid was as vigilant as it contends. American Cyanamid had an exclusive contract with the Chemical Control facility to handle all of its hazardous waste, including its PCB waste. It continued to utilize the services of this organization despite the presence of an excessive number of drums on the Chemical Corporation site, which in the words of Ralph Wainwright who, as an American Cyanamid Company’s supervisor of industrial hygiene and safety, was responsible for disposal of wastes, “bothered everybody”. In addition, American Cyan-amid Company made no further inquiries concerning Chemical Control despite the fact that Mr. Wainwright was aware of an incident in which Chemical Control was linked to barrels of waste which had been improperly disposed of on a vacant lot in Newark, New Jersey. I find that this defendant is responsible for ten drums of toxic hazardous material found at the site. Accordingly, this defendant is liable to the State as set forth, infra. Olin Corporation The following facts are undisputed: Richard S. Henley, manager of regional environmental affairs for Olin, visited the Picillo site on June 22,1982. At this time, Mr. Leo showed him five 55-gallon drums as having come from Olin. All but one of these drums either had a label of a product manufacturer addressing the drum to Olin, or the marking “Poly-G,” an Olin trade name. Mr. Henley was also shown a five gallon pail with a label designation “fatty acid” and a small cardboard container which contained four 4-inch vials — intact and not leaking. Mr. Henley did not identify the contents of other drums or containers. No PCBs (Polychlorinated Biphenals) at the site are attributable to Olin. I conclude that Olin was the generator of the contents of the five fifty-five gallon drums, the five-gallon pail, and the cardboard container. The question still pending is whether the plaintiff has carried the burden of proving the material was hazardous; all that the plaintiff offers on this point is its statement in its brief that “[t]he degree of toxicity of the individual waste may not have been determined but its status as a hazardous waste was confirmed by Mr. Leo through the code numbers on the waste and his discussions with Defendant representatives.” The pertinent portion of the transcript reference merely reflects Mr. Leo’s testimony that though samples of the materials were taken, no analysis was done and he could not identify the contents of the drums. When asked how, absent any analysis, he could label the material toxic, he replied, “[b]ased on the information on the outside of the label ... on the drum, and based on conferring with Olin representatives when they came out to the site to look at some of the drums.” As against this, the defendant presented the testimony of Dr. Steven Barber, Manager of Toxicology at Olin who stated that polyol, which was found in the 55-gallon drums, is not a hazardous substance as defined in section 101(14) of CERCLA. Dr. Barber also testified that Taluene diisocya-nate (TDI), when exposed to water, forms polyurea, which is not a hazardous substance as defined under CERCLA, and that fatty acids are also not a hazardous substance under CERCLA. This testimony was not refuted. I cannot accept Mr. Leo's general statement as sufficiently probative to find that Olin’s material was hazardous. Accordingly, I find that the State has failed to prove that the Olin materials were hazardous substances under CERCLA. Judgment must be entered for this defendant. Hydron Laboratories, Inc. This defendant generated a sodium aluminum hydride product known as Vi-tride which is a hazardous toxic material. In all of 1977, this defendant had a total of 28 barrels of its sodium aluminum hydride waste delivered to Chemical Waste Removal, Inc., a transporter for disposal. Twenty-one of these barrels were found at the site in question. The testimony is quite clear that nineteen of the barrels were intact, i.e., not leaking, and that two had pin holes which caused miniscule leaking of a few drops. The plaintiff argues that “several of the Hydron barrels suffered perforations ranging in size from pin hole-leaks to a hole the diameter of a dime” but offers no transcript reference supporting this statement. Mr. Leo’s cross-examination is of no help to the plaintiff, rather it corroborates the defendant’s contention of no leakage excepting for the pin holes. And the testimony established that “emission through small ‘pinhole’ leaks in drop quantities would result in evaporation so quickly that it could not pose any threat.” I find that twenty-one barrels of Hydron toxic hazardous waste with miniscule leaking were found at the site. I find this defendant did not contribute to the Picillo dump contamination but that the Hydron barrels posed a threatened release of the hazardous substance they contained. I find them liable. IV. SCOPE OF LIABILITY It is now quite well settled that liability under CERCLA is joint and several. See, e.g., United States v. South Carolina Recycling and Disposal, Inc., 653 F.Supp. 984, 992 (D.S.C.1986); Idaho v. Bunker Hill Co., 635 F.Supp. 665, 676 (D.Ind.1986). If the injury is indivisible, then each defendant is responsible for the entire cost. United States v. Chem-Dyne Corp., 572 F.Supp. 802, 811 (S.D.Ohio 1983). If, however, the injury is divisible or there is nonetheless a reasonable basis for division according to the contribution of each, then liability will be apportioned accordingly. Restatement (Second) of Torts sections 433A & 881 (1976). The defendant carries the burden of demonstrating that the injury is divisible or otherwise subject to apportionment. United States v. Dickerson, 640 F.Supp. 448, 450 (D.Md.1986). The defendants assert that there are two supportable ways to apportion liability. The first involves segregating the Picillo site essentially into four separate and distinct harms correlating with the four stages of the clean up. The second involves focusing on the volumetric contribution of each defendant as indicated by the number of drums attributable to each found at the site. The cleanup of the Picillo site began in 1979 and lasted until 1982. As this litigation proceeded, the four years of excavation became known as four separate “phases”: phase 0 represented the work completed in 1979, phase I represented the work completed in 1980, and so on. Each phase, moreover, involved work on different areas of the site. During phase I, for example, which spanned 1980, a trench in the northeast area of the site was excavated. Phases II and III, which followed, involved excavation of trenches in the northwestern, western, and southern areas of the site. The state retained different contractors for each phase. The defendants now urge that liability should be apportioned according to these four separate phases. They contend, for example, that because neither Rohm & Haas nor American Cyanamid drums were discovered during phases O or I, the costs of cleanup during these phases should be excluded from any liability calculation and the actual liability to these defendants should be reduced accordingly. I have trouble with this argument. The fact that the cleanup of the Picillo site proceeded in four stages does not necessarily render the underlying injury divisible. In fact, the manner in which the state conducted the cleanup, whether in one, two, or a hundred stages, is practically and theoretically immaterial to the question of whether the devastated state of the Picillo property can be divided into distinct harms. In fact, the defendants acknowledge in their brief that this is an untenable basis for apportioning liability. After suggesting that dividing liability among the phases is a rational way to apportion costs, they in fact reject this method when they describe its application. For example, defendants refer to phase III, during which 3300 drums of toxic waste were discovered, and contend that of that number, only 24 are attributable to Rohm & Haas. They contend that since that number constitutes .07% of the total, Rohm & Haas should be liable for .07% of the costs of Phase III. It is clear from this that the various phases of the cleanup are virtually irrelevant to the proferred apportionment calculation and the defendants seek to apportion liability solely on the basis of the number of drums found at the site. Finally, dividing the costs solely on the basis of which phase the defendant’s waste was discovered is inconsistent with recent decisions concerning the scope of liability under CERCLA. As one court held: A CERCLA defendant’s liability under section 107(a) is not restricted to the cleanup of those hazardous substances directly attributable to it. Rather, once the Government has proven that a defendant’s waste is present at a site and that the waste contains hazardous substances, the defendant may be held jointly and severally liable for the entire cost of removal and remedial actions required at the site not inconsistent with the National Contingency Plan. United States v. New Castle County, 642 F.Supp. 1270, 1276 (D.Del.1986). The defendant’s second proffered basis for apportionment, which, it appears, is implicit in the first, is to divide liability according to the number of drums found at the site that can be attributed to the defendants. They argue that a defendant who has contributed, say, one per cent of the total number of drums should be liable for one per cent of the costs of cleanup. There is no question that the number of drums may be an appropriate criterion for apportioning liability if all of the drums contained identical wastes. See Developments, Toxic Waste Litigation, 99 Harv.L. Rev. 1458, 1528 (1986). In such a case, there is “the reasonable assumption that the respective harm done is proportionate to that number.” Restatement (Second) of Torts section 433A, comm, d (1976). However, “the volume of waste of a particular generator is not an accurate predictor of the risk associated with the waste because the toxicity or migratory potential of a particular substance generally varies independently of the volume.” Chem-Dyne Corp., 572 F.Supp. at 811. Thousands of dented and corroded drums containing a veritable potpourri of toxic fluids were discovered at the Picillo site. Many were found intact but many had ruptured spilling chemicals into the soil. Some were discovered empty, having already discharged their contents. I find, that it is simply impossible to determine which defendant’s waste contributed in what specific manner to the releases and continuing threat of further releases. Under these circumstances, where different substances possessing different qualities of toxicity and migratory potential commingle, there is a synergistic impact upon the environment that necessitates a finding that the consequent injury is indivisible. See United States v. Stringfellow, 661 F.Supp. 1053, 1060 (C.D.Cal.1987); United States v. South Carolina Recycling and Disposal, Inc., 653 F.Supp. 984, 994 (D.S.C.1984). I therefore hold that the injury to the Picillo site is indivisible and the defendants are jointly and severally liable for the costs of the cleanup. I am not insensitive to the possible unfairness involved in holding a few relatively small contributors jointly and severally liable for the entire harm. Indeed, there is no question that in CERCLA actions, like other actions involving joint tortfeasors, a court may consider equitable factors to apportion damages and mitigate the effects of joint and several liability. I believe, however, that issues of fairness and equitable apportionment may be more properly addressed in a subsequent contribution action, which apparently Rohm & Haas and American Cyanamid have already begun. See Restatement (Second) of Torts section 881(1) & (2) (“equitable shares of the liability with respect to an indivisible injury are appropriately resolved in an action for contribution”). This is consistent with CERCLA’s key objective of “facilitatfing] the prompt cleanup of hazardous dumpsites by providing a means of financing both governmental and private responses, and by placing the ultimate financial burden upon those responsible for the danger.” City of Philadelphia v. Stephan Chemical Co., 544 F.Supp. 1135, 1142-43 (E.D.Pa.1982). By delaying thorny considerations of equitable apportionment to a later contribution proceeding, the government is provided immediate funds after the initial liability hearing to take prompt remedial action at the earliest opportunity. Garber, Federal Common Law of Contribution Under the 1986 CERCLA Amendments, 14 Eco.L.Q. 365, 369 (1987). In most instances, immediate response to potential disasters caused by seepage and migration can forestall the accrual of considerably higher compensation costs. Note, Allocating the Costs of Hazardous Waste Disposal, 94 Harv.L. Rev. 584, 587 (1980). As one court has observed: It is helpful to note that the purpose of CERCLA is environmental protection, including protection of public health and safety. Imposing joint and several liability carries out the legislative intent by ensuring that responsible parties will fulfill their obligations to clean up the hazardous waste facility. The court has discretion to use equitable factors in apportioning damages in order to mitigate the hardships of imposing joint and several liability upon defendants who have only contributed a small amount to a potentially large indivisible harm. However, the court’s discretion in apportioning damages among the defendants during the contribution phase does not effect the defendant’s liability. Stringfellow, 661 F.Supp. at 1060; see also United States v. New Castle, 642 F.Supp. 1258, 1277 (D.Del.1986) (“CERCLA places the burden of apportioning blame on the defendants by way of actions for contribution and apportionment.”). V. DEFENSES Unclean Hands In Violet, I held that because plaintiffs in CERCLA actions seek the equitable remedy of restitution, defendants were entitled to raise equitable defenses. 648 F.Supp. at 1294-95. The defendants argue in their post-trial brief that the first stage of the Picillo cleanup was mishandled and that the doctrine of unclean hands consequently bars the state from recovering the cost of the cleanup. The evidence presented during trial revealed that the so-called phase I excavation was characterized by inadequate record-keeping and possibly improper removal methods, which resulted in excess spillage. Testimony indicated that the state’s contractor for phase I, Jet Line Services, Inc. (Jet Line), a novice at this sort of venture, used backhoes with teeth to excavate the drums, often puncturing the drums and causing their contents to spill onto the ground. Testimony by one of the defendant's experts indicated that more appropriate methods, including the use of barrel grapplers, which have been available for decades, could have prevented much of the spillage. There was also evidence that Jet Line was initially compensated on a per-drum basis, encouraging haste without regard to safety and conservation. Only after many drums had been destroyed in the process did the State finally amend the contract to force Jet Line to employ less destructive methods. Finally, if records were kept during phase I, and it is conceivable that as a result, some generators are not now before this court. In defense, the state points to testimony that spillage is inevitable in any cleanup project. One of the state’s employees testified that such hazardous waste cleanup projects were just beginning at the time phase I was conducted and thus the “state-of-the-art was at a fledgling level.” As to this contract with Jet Line, the state contends — and testimony supports its contention — that it agreed to Jet Line’s per-drum compensation scheme because an independent consulting corporation had estimated that there were only a few hundred barrels of waste to be removed. Later, when it became clear that there were thousands more barrels than anticipated, the state amended the compensation schedule and threatened to close down the project unless Jet Line improved its methods. The doctrine of unclean hands is a recognition of the maxim that “he who seeks equity must do equity.” Rather than constituting a defense to liability in the traditional sense, the doctrine is applied in the public interest and to protect the integrity of the court by foreclosing the possibility that the court will assist a wrongdoer. As one court described the doctrine: In the interests of right and justice the court should not automatically condone the defendant’s infractions because the plaintiff is also blameworthy, thereby leaving two wrongs unremedied and increasing the injury to the public. Rather the court must weigh the substance of the right asserted by the plaintiff against the transgression which, it is contended, serves to foreclose that right. The relative extent of each party’s wrong upon the other and upon the public should be taken into account, and an equitable balance struck. Republic Molding Corp. v. B.W. Photo Utilities, 319 F.2d 347, 350 (9th Cir.1963). Evidence of some misconduct by the plaintiff, therefore, is not an automatic bar to recovery; rather, a district court has “wide latitude to compare the cleanliness of the parties ‘hands’.” United States v. Zenon, 711 F.2d 476, 478 (1st Cir.1983) see also Precision Instrument Mfg. Co. v. Automotive Maintenance Machinery Co., 324 U.S. 806, 815, 65 S.Ct. 993, 997, 89 L.Ed. 1381 (1945) (the unclean hands doctrine “necessarily gives wide range to the equity courts use of discretion in refusing to aid the unclean litigant. It is not bound by formula or restrained by any limitation that tends to trammel the free and just exercise of discretion.”). After carefully considering the state’s conduct during the early stages of the cleanup, I conclude that it does not so soil the state’s hands that recovery is barred in this action. My conclusion is informed not only by a balancing of the equities in this case, but also by the simple fact that courts have uniformly held that mere negligence on the part of the plaintiff is insufficient to bar relief under the unclean hands doctrine. See Shearson/American Express, Inc. v. Mann, 814 F.2d 301, 307 (6th Cir.1987); Pfizer, Inc. v. Int’l Rectifier Corp., 685 F.2d 357, 359 (9th Cir.1982), cert. denied, 459 U.S. 1172, 103 S.Ct. 818, 74 L.Ed. 2d 1016 (1983); International Union, Etc. v. Local Union No. 589, 693 F.2d 666, 672 (7th Cir.1982); Bresh v. Braecklein, 133 F.2d 12, 14 (10th Cir.1943). Therefore, even if I were to conclude that the state was negligent during the initial stage of the cleanup, that conclusion would be insufficient to trigger application of the doctrine of unclean hands. Third-Party Defense CERCLA section 107(b), in relevant part, provides: There shall be no liability under subsection (a) of this section for a person otherwise liable who can establish that the release or threat of release of a hazardous substance and the damages resulting therefrom were caused solely by— (3) an act or omission of a third party other than an employee or agent of the defendant, or than one whose act or omission occurs in connection with a contractual relationship, existing directly or indirectly, with the defendant— 42 U.S.C. section 9607(b). A defendant may invoke this defense if he can also show that he “exercised due care with respect to the hazardous substances concerned and took precautions against any acts or omissions of the third party and any consequences foreseeably flowing from those acts or omissions.” Violet, 648 F.Supp. at 1293; see 42 U.S.C. section 9607(b)(3)(a)-(b). The defendants argue that they are entitled to this defense because they consigned their wastes to licensed waste transporters and there is no evidence that these transporters had any contact with the Picillo site. Therefore, they contend, “whatever party was responsible for transporting the [defendants’] waste to the Picil-lo site had no direct relationship with [the defendants] and there is no evidence of any other relationship, indirect or otherwise.” I find that the defendants have failed to meet the initial showing that the release was caused solely by a party that did not have either a direct or indirect contractual relationship to the defendants. The simple fact is that during the time the defendants consigned their waste to licensed disposers, some of that waste, in indentifiable containers, came to rest at the Picillo site. The defendant’s argument that there was no evidence linking the disposers to the site or that the defendants had any relationship with whomever actually deposited the waste there simply confuses the nature of its burden under the third-party defense. As I stated in Violet, the third-party defense “essentially serve[s] to shift the burden of proof of causation to the defendants.” 648 F.Supp. at 1293. The defendants must demonstrate by a preponderance of the evidence that “a totally unrelated third party is the sole cause of the release.” Stringfellow, 661 F.Supp. at 1053; see Dedham Water Co. v. Cumberland Farms Dairy, Inc., 805 F.2d 1074, 1079 n. 10. (1st Cir.1986). Absent any evidence along these lines, I must conclude that it is equally likely that either the licensed disposers or a subcontractor of the disposers deposited the waste at the site. The defendant’s argument appears to be a repackaging of the argument that a generator can escape liability merely by showing that it had in fact arranged to have its waste dumped elsewhere. This argument, however, was not only rejected in Violet, see 648 F.Supp. at 1291, but by other courts as well. See, e.g., United States v. Ward, 618 F.Supp. 884, 895 (E.D.N.C.1985) (section 107 does not require that the arrangement include knowledge of the ultimate disposal site); Missouri v. Independent Petrochemical Corp., 610 F.Supp. 4, 5 (E.D.Mo.1985) (generators may be liable for costs at site though it expressly arranged to have its wastes delivered to another facility); United States v. Conservation Chemical Co., 619 F.Supp. 162, 234 (W.D.Mo.1985) (same). National Contingency Plan Persons held liable under section 107(a) of CERCLA are responsible for “all costs of removal or remedial action incurred ... not inconsistent with the National Contingency Plan.” 42 U.S.C. 9607(a). The Plan is set out in 40 C.F.R. Part 300, and in effect requires that the clean-up measures be cost effective. 42 U.S.C. 9605(7); 40 C.F.R. section 300.68(j); see J.V. Peters & Co., Inc. v. Administrator, E.P.A., 767 F.2d 263, 265 (6th Cir.1985); United States v. United Nuclear Corp., 610 F.Supp. 527, 529 (D.N.M.1985). Defendants argue that the state has failed to prove that its actions were consistent with the Plan. Specifically, they allege that Phase I of the cleanup was characterized by sloppy and inefficient practices that were not cost effective. As an initial matter, I hold that when a state government is pursuing response costs under CERCLA, the burden of proving that the cleanup was inconsistent with the Plan rests with the defendant. As one district court persuasively reasoned: Defendants argue that the plaintiff failed to prove that the costs incurred were reasonable and “not inconsistent with the national contingency plan.” Initially, the Court finds that the burden of proving inconsistency with the national contingency plan was that of the defendants. This conclusion is evidence from the language of the statute. To give meaning to every term in the statute, the Court reads the insertion of the word “not” immediately prior to “inconsistent” to mean that the defendants are presumed liable for all response costs incurred unless they can overcome this presumption by presenting evidence of inconsistency. The content of section 107(a)(4)(B) lends support to this conclusion in stating that responsible parties are liable for “any other costs of response incurred by any other person con sistent with the national contingency plan.” (emphasis added) On its face, section 107(a)(4)(B) intends that a different standard apply to cost recovery by non-governmental entities and that such entities must affirmatively show that their actions were consistent.... United States v. Northeastern Pharmaceutical and Chemical Co., 579 F.Supp. 823, 850-51 (D.Mo.1984); see United States v. South Carolina Recycling and Disposal, Inc., 653 F.Supp. 984, 1009 (D.S.C.1986). It is also clear from the statute that variance from the Plan does not provide a complete defense to liability. By its own terms, Section 107(a) bars “costs” that are inconsistent with the Plan, not “actions.” See, e.g., Lone Pine Steering Comm. v. United States, 600 F.Supp. 1487, 1499 (D.N.J.), aff'd 777 F.2d 882 (3d Cir.1985). Therefore, the defendants have the burden of demonstrating that the clean-up, because of some variance from the Plan, resulted in demonstrable excess costs for which they should not be responsible. The trouble with the defendant’s claim in this regard is that while they have presented evidence that the use of barrel grapplers, for example, or the employment of a different compensation scheme for the contractor, would have prevented some of the spillage that occurred during Phase I, they have not presented any evidence addressing how much of the recovery costs incurred by the state, as a result, should be precluded. While I am not unsympathetic to the defendants’ plight, I refuse to speculate as to how much recovery is too much. Accordingly, I find that the defendants have failed to prove that certain costs were inconsistent with the National Contingency Plan. Retroactive Application of CERCLA The defendants argue that the releases for which they are now being held to answer occurred prior to 1980, the effective date of CERCLA. They contend that to hold them liable for such conduct constitutes retroactive application of a statute in violation of due process. This argument has been thoughtfully analyzed and rejected by numerous courts. See United States v. South Carolina Recycling and Disposal, Inc., 653 F.Supp. 984, 996-98 (D.S.C.1986); United States v. Shell Oil Co., 605 F.Supp. 1064, 1072-73 (D.Col.1985); United States v. Northeastern Pharmaceutical and Chemical Co., Inc., 579 F.Supp. 823, 839-43 (D.Mo.1984); State ex rel. Brown v. Georgeoff, 562 F.Supp. 1300, 1309-1314 (N.D.Ohio 1983). I adopt the reasoning and conclusion of these courts and hold that liability for response costs under CERCLA for releases which occurred prior to 1980 does not offend due process. VI. SETTLEMENTS AND FUTURE LIABILITY Effect of Settlements On the day designated for trial, the State and the United States Environmental Protection Agency, a non-party, settled with numerous potential defendants. That settlement included a $2.3 million cash settlement to be applied to the past costs of the entire clean-up, as well as commitments from the settling defendants to perform future remedial work valued at $3.5 million. Of this, the State was to receive twenty-five per cent of the cash settlement, or $575,000.00. The State also independently settled with other defendants for $46,500, bringing the total amount of settlement proceeds to the state to $621,-500.00. A provision of the 1986 SARA amendments provides: A person who has resolved its liability to the United States or a State in an administrative or judicially approved settlement shall not be liable for claims for contribution regarding matters addressed in the settlement. Such settlement does not discharge any of the other potentially liable persons unless its terms so provide, but it reduces the potential liability of the others by the amount of the settlement. 42 U.S.C. section 9613(f). I conclude that under the express language of the statute the total liability for past response costs must be reduced by the amount the state received in cash settlement, i.e., $621,500.00. Therefore, Rohm & Haas, American Cyanamid, and Hydron are liable for past response costs in the amount of $991,937.30. The settlement also included a commitment by the settling defendants to perform future remedial work at the site. This work was valued at $3.5 million and involves the removal of the three piles of soil totaling 6,500 cubic yards which had been found to contain PCB’s and phenols. The defendants contend that the dollar value of this settlement arrangement must be applied to reduce their past response cost liability because there was no proof that the PCB pile constituted a hazardous waste that must be removed from the Pitillo site. They point out, for example, that there was uncontradicted testimony that the average concentration of the PCB pile was only about 36 parts per million and that under applicable state and federal regulations removal is not required below concentrations of 50 parts per million. Therefore, they argue, since removal of these piles is not actually required by law, the value of the agreed-upon removal, $3.5 million, must be applied to the response cost, thereby in effect satisfying all of the state’s clean-up costs. I reject this argument for the simple reason that the state’s success in negotiating a settlement as to the PCB and phenol piles at the site is irrelevant to the costs incurred during the initial excavation of the numerous drums and contaminants during the four stages of the clean-up. There is no question that a CERCLA plaintiff may settle with other potentially responsible parties for particular remedial action that is distinct from other response costs. See United States v. Northeastern Pharm. & Chem. Co., 579 F.Supp. 823, 831-32 (W.D.Mo.1984). Moreover, I fail to see why the fact that the settling defendants may not have been shown ultimately to be responsible for removing the contaminated soil piles has any significance. As one court confronted with a similar issue put it: Of course, the future may ultimately reveal that the settling generators have compensated the federal government for claims on which the government would not have prevailed. This is simply the risk inherent in all settlements. United States v. Wade, 577 F.Supp. 1326, 1337 (E.D.Pa.1988). Declaratory Judgment As To Future Liability The state seeks a declaratory judgment seeking entitlement to recover its future response costs associated with the Pi-tillo site. It argues that toxic chemicals have been released into the groundwater and that the EPA is currently conducting extensive testing as to any possible damage that would require response costs. I believe that this is an appropriate case for declaratory judgment. The issues have been firmly established and there is a real, present controversy between the plaintiff and defendants. See C. Wright & A. Miller, Federal Practice and Procedures section 2759 (2d ed. 1983); Conservation Chem. Co., 619 F.Supp. at 211. Further, the courts are unanimous that declaratory judgments as to future removal costs are consistent with CERCLA’s purpose of encouraging prompt, remedial action. See e.g., id. at 211-12; Northeastern Pharm. & Chem. Co., 579 F.Supp. at 852-53; Georgeoff, 562 F.Supp. at 1316. Accordingly, I conclude that the defendants are jointly and severally liable for all future costs of removal or remedial action incurred by the state relative to the Pitillo site that are not inconsistent with the National Contingency Plan. This ruling includes any costs associated with the removal of the contaminated soil piles which the state may incur despite commitments by the settling defendants to remove the piles. I recognize that defendants have argued forcefully that they did not contribute PCB’s or phenols to the Pitillo site. However, because I have ruled that the defendants are jointly and severally liable for the Picillo disaster, it follows that they are . liable for all response costs associated with it. See New Castle County, 642 F.Supp. at 1319 (a CERCLA defendant’s liability, once it is found that the injury is indivisible, “is not restricted to the cleanup of those hazardous substances directly attributable to it