Bob's Beverage, Inc. v. Acme, Inc. (169 F. Supp. 2d 695, 1999)

MEMORANDUM AND OPINION

HEMANN, United States Magistrate Judge.

OUTLINE OF MEMORANDUM AND OPINION

703 I. Background.

703 A. Development of the site.

704 B. Tenantship at the site by Acme.

704 1. Operations.

706 2. Drum storage.

707 C. Tenantship at the site by Albatross_

707 1. Drum storage.

708 2. Drains and septic disposal.

709 3. Oil contamination.

709 D. Ownership of the site by Bob’s Beverage

710 711 E. Contamination by CVOCs . II. Summary judgment standard.

712 III. Plaintiffs’ motion for summary judgment.

712 A. Claim under 42 U.S.C. § 9607(a).

712 1. The two causes of action.

2. PRPs, the third party defense, and availability of action under § 9607(a) . 713

3. Plaintiffs and the third party defense. 714

a. Third party sole cause of the release. 714

b. Release not in connection with a contractual relationship . 714

c. Precautions against foreseeable acts or omissions of third party 715

d. Exercise of due care with respect to hazardous substance. 715

Elements of a cause of action authorized by 42 U.S.C. § 9613(f). 717 w

Summary judgment as to issues raised under § 9613(f). 717 o

1. Whether the properties at 9810 and 9812 East Washington Street and contiguous properties contaminated by CVOCs are a “facility” 717

2. Whether the CVOCs found at the site are hazardous substances. 717

3. Whether the defendants are “persons” for purposes of liability under § 9607(a) . “3 M OO

4. Whether a release or threatened release has occurred . -Q H CD

5. Whether the release caused plaintiffs to incur response costs. r-jj W O

6. Whether the incurred response costs are necessary and consistent with the NCP . 720

7. Whether all defendants are liable for contribution under § 9613(f) because they fall within a category of persons who are liable under § 9607(a) . — CO

a. “Owner or operator”. -«3 to

b. “Disposal” . «<] to

c. Liability of defendants as owners or operators at the time that hazardous substances were disposed of.

1. Liability of defendant Acme.

2. Liability of defendant Bares .

a. Direct liability as operator.

b. Derivative liability as corporate officer.

S. Liability of defendants B. Merkel and H. Merkel .

а. Direct liability as owners.

б. Derivative liability as partners.

IV. Defendants Acme and Bares’ joint motion for summary judgment.

A. Whether the court should “pierce the corporate veil” of Acme to find Bares indirectly liable for Acme’s acts under CERCLA. -3 to Ol

B. Whether Acme is a viable party in this litigation. -3 to Oi

C. Whether Bares violated Ohio Rev.Code § 1701.88(A) or § 1701.97. -3 to <]

D. Whether Acme and Bares violated CERCLA as operators of the facility -3 to CO

V. Joint motion for summary judgment of defendants Albatross and the Merkels -3 to

A. Whether defendants are not liable because only active conduct which causes contamination can trigger CERCLA liability for response costs -3 to CO

1. Liability under § 9701(a)(1) . <3 to CO

a. Liability as owners of the site as set forth in § 9607(a)(1). -a to CO

b. Liability as operators of the site as set forth in § 9607(a)(1). -3 to CO

2. Liability under § 9607(a)(2) . -3 CO O

a. Liability as owners of the site as set forth in § 9607(a)(2). -3 CO o

b. Liability as operators of the site as set forth in § 9607(a)(2). -3 CO I — I

B. Whether Albatross is not liable for response costs under CERCLA because Albatross did not dispose of any hazardous substance or hazardous waste. -a CO to

VI. Conclusion. -3 CO to

This matter is before the magistrate judge pursuant to consent of the parties. Plaintiffs commenced this action pursuant to the Comprehensive Environmental Response, Compensation and Liability Act (“CERCLA”). Before the court are the motion of plaintiffs, Bob’s Beverage, Inc. (“Bob’s Beverage”) and Ullman Oil, Inc. (“Ullman Oil”), for summary judgment (“Pl.Mot.,” Docket # 85), the motion of defendants Acme, Inc. (“Acme”) and James D. Bares (“Bares”) for summary judgment (“Def.Mot.,” Docket # 102), and the motion of defendants Albatross, Ltd. (“Albatross”), Benjamin Merkel (“B.Merk-el”), and Henry H. Merkel (“H.Merkel”) for summary judgment (Docket # 84). For the reasons set forth below, the court grants plaintiffs’ motion in part and overrules it in part; grants the motion of defendants Acme and Bares in part and overrules it in part; and overrules the motion of defendants Albatross, B. Merkel, and H. Merkel.

I. Background

A. Development of the site

In 1960 Cleo Gastemire sold to Ray and Nancy Hitchcox undeveloped farmland which is presently property at 9810 and 9812 East Washington Street, Chagrin Falls, Ohio. The Hitchcoxes established a store on the property at 9810 East Washington Street. That store, currently known as “The Hitchin’ Post,” is both a convenience store and service station. Deposition of Kim A. Ullman, Def.Mot., Defendants’ Joint Appendix of Exhibits (“Def.App.”), Exh. F, pp. 71, 93-94. The Hitchcoxes sold the 9810 East Washington Street property in 1972 to Marilyn Ullman. The property later came into the possession of Bob’s Beverage, a corporation owned by members of the Ullman family. Id. at 21, 83-84.

In approximately 1973 the Hitchcoxes erected a building (“the building”) on the 9812 East Washington Street property (“the site”). The Hitchcoxes leased space in the building to various tenants in the early 1970’s. The record does not describe the activities in which these tenants engaged while at the site.

The Hitchcoxes installed a septic system for the building. The system as approved consisted of four-inch pipe which ran from a drinking fountain and toilet to two 1,000-gallon septic tanks in series and then to two 1,000-gallon dry wells in series. Application of John Blazek on behalf of Ray Hitchcox for a sewerage and well permit, Plaintiffs Revised Appendix Filed in Support of Motion for Summary Judgment (“PLApp.”) (Docket # 104), Exh. 1, p. 3. The system was designed to leach effluent which reached the dry wells into the surrounding soil. Deposition of Frank Szoka (“Szoka”), Def.App., Exh. H, pp. 16-17.

B. Tenantship at the site by Acme

In 1974 Acme became a tenant in the building. Acme reconditioned automotive air conditioning equipment, and Bares was its president and sole owner. Plaintiffs First Request for Admissions Propounded to Defendant James D. Bares, Pl.App., Exh. 2, p. 3; Deposition of Bares, Def. App., Exh. K, p. 23, 24.

1. Operations

Acme altered the building when it became a tenant. The alterations included cutting drainage ditches into the concrete floor for moving chemicals, wash water, and other waste materials away from work areas. Affidavit of Paul C. Mason (“Mason”), Pl.App., Exh. 5, p. 4. According to William Burke (“Burke”), the technical director of operations for Acme at the site, the material that drained into the ditches was soapy water, harmless abrasive grit, and chemicals washed from parts taken from a caustic soda wash. Deposition of Burke, Def.App., Exh. 0, pp. 27-28, 35, 37-38, 45-46. Bares admitted that the rinse water from Acme’s operations was discharged into the septic system and that it had been used to wash parts coming from the caustic soda tank. Letter of Apr. 13, 1979 from Bares to the Ohio Environmental Protection Agency (“Ohio EPA”), Pl.App., Exh. 3; Def.App., Exh. K, pp. 92-93. Mason, who worked for Acme during the summer of 1974 and then full-time from 1975 until 1978, asserts that the waste water included solvents. Pl.App., Exh. 5, p. 4. Acme originally disposed of this waste water by emptying it into the septic system. Pl.App., Exh. 3, p. 1; Def. App., Exh. K, pp. 72-73; Exh. 0, pp. 26-28, 35, 37-38, 58. By 1979 Acme disposed of the waste water by dumping it onto the surface, from which it eventually entered tributaries of the Chagrin River. Application for permit to discharge, Pl.App., Exh. 4; Def.App., Exh. K, pp. 92-93.

Employees disassembled old air conditioning units at “tear down” tables. According to Mason, “Any refrigerants or oils that were in the units would spill onto the tear down tables and the spilled material was collected in a drum at the end of the tables. When full, the drum would be taken outside and placed in the drum storage area.” Pl.App., Exh. 5, pp. 5-6. Bares claims that only oil was collected at tear down tables and that it was stored in a 55-gallon drum inside the building for reclamation. Def-App., Exh. K, p. 89, 102.

Cleaning the disassembled parts involved a variety of hot and cold chemical baths and washes. One bath involved a “triehlor tank.” Mason remembers that this tank held 30 to 55 gallons of solvent and had heating elements at the bottom. PLApp., Exh. 5, p. 4. Bares asserts that it held no more than 30 gallons of solvent. Def.App., Exh. K, p. 83. The tank originally used trichloroethylene as its cleaning solvent. PLApp., Exh. 5, p. 4; Def.App., Deposition of Mason, Exh. M, p. 21; Exh. K, p. 88. Mason claims that the tank later used 1,1,1-trichloroethane. PLApp., Exh. 5, p. 4; Def.App., Exh. M, p. 21. Bares avers that the trichloroethylene was replaced by a detergent containing no chlorinated volatile organic compounds (“CVOCs”). Def.App., Exh. K, p. 92. David Felger (“Felger”), who was a shop foreman for Acme while it was at the site and who currently works for a company owned by Bares’ niece, remembers the triehlor tank as containing 1,1,1-trichlo-roethene and has no memory of trichloro-ethane. Deposition of Felger, Def.App., Exh. L, pp. 47-48; Exh. K, pp. 18, 38; Exh. M, p. 27.

About every two months spent solvent was scooped out of the triehlor tank and into 55-gallon drums. PLApp., Exh. 5, p. 4. Mason asserts that these “drums were placed outside in the drum storage area.” Id. Bares, Burke, and Felger claim that the drums were kept inside the building until they were sold back to the suppliers for reclamation. Def.App., Exh. K, pp. 57-59, 82-83; Exh. L, pp. 52, 58-60, 68; Exh. O, pp. 11, 52.

Another heated bath used a 80- to 90-gallon mixture of water and caustic soda (i.e. sodium hydroxide). PLApp., Exh. 5, p. 5. The Environmental Protection Agency lists sodium hydroxide as a hazardous substance. 40 C.F.R. § 302.4. Mason remembers that parts removed from the caustic soda bath were washed or scrubbed, and the waste liquids spilling from the parts ran into drains in sinks or in the concrete ditches. PLApp., Exh. 5, p. 5. Felger denies that caustic waste was washed into the ditches, but he does not remember what did happen to the spilled liquid. DefApp., Exh. L, pp. 66-67, 73. Waste pumped from the caustic soda bath “was handled in much the same way as the waste from the [triehlor] tank,” according to Mason. PLApp., Exh. 5, p. 5. Bares asserts that the caustic waste tank was pumped out by a local septic tank cleaner when the tank was cleaned. Def.App., Exh. K, p. 59. He “guesses,” however, that residue of caustic soda was included in material pumped into the septic system. Id. at 78-79.

Acme also used other unidentified chemicals and solvents. PLApp., Exh. 5, p. 5. At least one naptha-like solvent was purchased from Ullman Oil next door to the site and brought over in 55-gallon drums by forMift. Def.App., Exh. M, pp. 17-19.

Mason claims that parts were “power washed” after removal from the baths. PL App., Exh. 5, p. 6. The power washing flushed the “various solvents and chemicals” on the parts from the baths “into the floor drains with concrete bottoms,” according to Mason. Id. Burke denies that any solvents were ever introduced into the septic system. Def-App., Exh. O, p. 67.

Mason claims that on one occasion he saw a hose run from the caustic tank or a cold stripper tank to siphon chemicals out of a window and onto the ground outside. DeflApp., Exh. M, pp. 31-35. He contends that he went outside a few days later and saw the vegetation dead where the chemicals had been dumped from the siphon. Id. at 36. Bares, Burke, and Felger deny that any chemicals were ever drained outside by siphon, although Burke says that clean water which cooled the triehlor tank might have been siphoned outside. Def. App., Exh. 0, p. 74.

2. Drum storage

According to Mason Acme transferred to the site 12 to 18 55-gallon drums when it became a tenant in the building. PL App., Exh. 5, p. 1; Def.App., Exh. K, pp. 56-57; Exh. M, pp. 30, 55-56. These drums had been stored at a property at Chagrin Road at which Acme had been conducting operations prior to leasing space in the building. PLApp., Exh. 5, p. 2; Def.App., Exh. K, pp. 56-57. Mason avers that the drums were full of spent and new solvents and other chemicals which Acme had generated at the Chagrin Road property and that some of the drums were “deteriorated” when Acme moved them. Pl.App., Exh. 5, pp. 1-2. Felger says that only 10 to 15 drums were moved and contends that the drums contained air conditioning compressors waiting to be torn down and rebuilt, miscellaneous junk, and some solvents. Def.App., Exh. L, p. 17.

Mason also asserts that the drums containing spent solvents and chemicals which were moved to the site “were placed outside, near the back of the East Washington Street building regardless of their existing condition.” Pl.App., Exh. 5, p. 2; see also Def.App., Exh. M, pp. 28-29. Felger says that three or four drums were stored outside but that none of the barrels contained solvent or oil. Def.App., Exh. L, pp. 18, 33, 36-37, 64. Bares also contends that no barrels containing chemicals were stored outside. Def.App., Exh. K, pp. 57-58. Burke asserts that the outside barrels had compressor parts in them, not liquid, and that no barrels with solvent in them were “deteriorated.” Def.App., Exh. 0, p. 66. Robert Halcik (“Halcik”), a salesman for Acme while it was at the site, also denies seeing liquid other than rainwater in the barrels. Deposition of Halcik, Def.App., Exh. P, p. 24.

Drums filled with spent solvent and other waste chemicals generated by Acme at the site were “placed in the same area as the drums from the Chagrin Road facility,” according to Mason. PLApp., Exh. 5, p. 2. Mason asserts, “While I worked for Acme these drums were never moved once they were placed there. I saw some drums that had rusted through and other drums that were seeping their contents from the top in the outside drum storage area.” Pl. App., Exh. 5, p. 6. Mike Cathan, who worked for Acme at the site, also claims that drums containing liquid were stored outside the building. Deposition of Ca-than, Def.App., Exh. N, pp. 11-12,18.

Bares asserts that no spent solvents were placed outside the building. Def. App., Exh. K, pp. 59-61. According to Bares all chemical wastes except the caustic soda waste were kept in drums inside the building until they were reclaimed by the chemical suppliers. Id. at 58-59. Fel-ger agrees that no drums containing liquid were kept outside the building. Def.App., Exh. L, pp. 27, 63-64. Burke denies that drums containing solvent were ever stored outside. Def.Ápp., Exh. 0, p. 24.

At one time, Mason says,

a fork lift driver punched through a drum full of chemical waste while adding drums to the outside drum storage area. The contents of the drum was [sic] released though the puncture in the drum onto the bare ground. To the best of my knowledge the spilled material was never cleaned up and the remaining contents of the drum were not transferred to a drum in good condition.

PLApp., Exh. 5, p. 2; see also Def.App., Exh. M, pp. 59-60. Bares does not recall such an incident. DefApp., Exh. K, pp. 62-63. He admits that some outside drums may have been pierced by a forklift but contends that because all outside drums contained solid metal compressor cores, no leak of waste material could have resulted from such an accident. Id. at 62-64. Felger says that he saw drums with compressor parts or junk in them pierced by a forklift but not drums containing liquid. Def.App., Exh. L, pp. 27, 63-64.

Mason claims that on at least one occasion he reported to Burke that drums were on their sides or leaking. PLApp., Exh. 5, p. 5. Mason did “not recall any action that was taken in response” to his report to Burke. Id. Mason avers that Burke “had personal knowledge of the drum conditions” and that Burke “reported directly to Jim Bares, the President of Acme.” Id. Bares denies that Burke ever told him about such an event. Def.App., Exh. K, pp. 67-68.

Mason says that on at least one occasion he reported to Halcik that drums in the outside storage area were on their sides or leaking. PLApp., Exh. 5, p. 5. Mason claims that “Halcik did not instruct [Mason] or to the best of [Mason’s] knowledge, anyone else to remedy the situation.” Id. Bares denies that Halcik ever told him about such an event. Def.App., Exh. K, pp. 68.

Mason claims that Bares had personal knowledge of the operations and drum storage at the facility. PLApp., Exh. 5, p. 3. Felger asserts that Bares was at the site daily, was never absent from the company for a long time, had an office at the site, and was involved in operations at the site. Def.App., Exh. L, pp. 21, 22-23, 24, 69. Burke contends that Bares managed operations at the site, that he knew and approved of how the hazardous chemicals were handled at the site, and that he could have directed that the chemicals be handled differently. Def.App., Exh. O, pp. 12, 33, 64-65. Bares denies involvement in the daily operations of Acme. PLApp., Exh. 2, p. 3.

C. Tenantship at the site by Albatross

Acme left the site in approximately 1980. PLApp., Exh. 2, p. 4. In 1980 Huntington National Bank of Burton, Ohio (“Huntington”) filed a foreclosure action against the Hitchcoxes. Huntington bought the site on September 3, 1981 at a sheriffs sale.

Huntington sold the property on August 13, 1982 to Albatross, Ltd. of Chagrin Falls, Ohio. Albatross was a limited partnership consisting of B. Merkel, H. Merkel and Lawrence Vail (“Vail”) which stored antique cars at the site. Deposition of H. Merkel, Def.App., Exh. Q, p. 14. B. Merk-el claims that none of the partners used solvents at the site. Deposition of B. Merkel, DefApp., Exh. R, p. 62. Albatross did not perform an environmental inspection of the site before buying it. Id. at 14-15, 17-18; Def.App., Exh. Q, pp. 26-27.

1. Drum storage

Bares claims that the auctioneers ordered everything that was outside the building brought inside for sale at the public auction upon Huntington’s foreclosure. Def.App., Exh. K, p. 102. Szoka, an excavator, remembers that about 100 55-gallon drums remained on the property after Albatross bought it. Deposition of Szoka, Def.App., Exh. H, pp. 20-22, 48. H. Merkel remembers about 9 to 12 drums by the loading dock outside the building, and about 4 to 6 other drums scattered around the outside lot. Def.App., Exh. Q, pp. 29-33, 107. B. Merkel remembers about eight drums by the loading dock and 3 or 4 scattered elsewhere on the lot. Def.App., Exh. R, p. 20. Photographs taken after Albatross took possession confirm that some drums were scattered on the property; the photographs do not show the loading dock. DefiApp., Exh. Q, pp. 69-71.

H. Merkel remembers three of the outside drums as containing rainwater. Id. at 29-31, 108; DefiApp., Exh. R, p. 23. One of these drums was emptied into Ullman Oil’s waste storage tank. Def.App., Exh. Q, pp. 30-31, 108-09; Exh. R, pp. 20-21. The others were dumped at the site. Def. App., Exh. Q, pp. 30-32; Exh. R, pp. 60-61.

According to the Merkels about four drums were filled with what appeared to be thick, viscous lubricating oil. Id. at 32, 64, 117, 120-21; Def.App., Exh. R, p. 20. These were covered and intact, and they were eventually pumped out and their contents disposed of by Research Oil Company (“Research Oil”) in September, 1987. DefiApp., Exh. Q, pp. 32, 64; Exh. R, pp .. 60-61. Research Oil identified the substance pumped with the initials “WW/WO.” DefiApp., Exh. Q, pp. 114-15.

The Merkels also assert that about three drums were partially filled with apparently the same material as the four full drums pumped by Research Oil. Id. at 120-21; Def.App., Exh. R, pp. 21-22. They say that the material in these drums was consolidated into a single, nearly-full drum, and that drum was also pumped by Research Oñ. DefiApp., Exh. Q, p. 121; Exh. R, p. 21, 60-61. The Merkels also claim that none of the drums containing the oil-like substance was leaking. DefiApp., Exh. Q, p. 32; Exh. R, p. 22.

H. Merkel asserts that the remaining outside drums were either empty or filled with trash. Id. at 32-33. He says that they had no sludge or coating in them. Id. at 81,122.

H. Merkel recollects that there were about 6 to 8 drums inside the building when Albatross occupied it; B. Merkel remembers 5 or 6. DefiApp., Exh. Q., pp. 27,101; Exh. R, p. 19. Some of the drums contained trash; others contained auto parts. DefiApp., Exh. Q., pp. 28, 102; Exh. R, p. 18-19. H. Merkel also remembers that one drum contained what appeared to be fresh lubricating oil and that it too was pumped by Research Oil in September, 1987. DefiApp., Exh. Q, pp. 28, 64, 126. H. Merkel asserts that none of the drums contained anything which “even remotely” could have been a solvent. Id. at 102.

2. Drains and septic disposal

Albatross found a channel about eight to ten inches wide, four inches deep, and six feet long cut near the middle of the concrete floor of the building. Id. at 42^3. It also found a “floor drain,” described as a trench covered by a metal grate, running east-west for almost the length of the building. Id. at 44; DefiApp., Exh. R, p. 26. Photographs taken after Albatross took possession of the property are consistent with the existence of these trenches as described. Id. at 74-75.

Albatross contracted with Szoka or Szo-ka Excavating to replace the existing septic system at the site with one approved by the Ohio EPA. Def.App., Exh. H, pp. 9-11; Exh. Q, p. 51-52. The existing septic system was not operational. DefiApp., Exh. H, pp. 6-18; Exh. Q, pp. 36-37, 51-52; Exh. R, pp. 31-32. The drywells which had been built to accept septic effluent and leach it into the ground would no longer accept the effluent because the soil in which the drywells had been sited contained too much clay to allow the effluent to leach properly from the drywells. Def. App., Exh. H, pp. 27-29.

Szoka installed the new septic system in 1984. DefiApp., Exh. Q, p. 81. He found that a pipe had been installed in the septic system to allow the effluent to bypass the dry wells and empty into a ravine and watercourse at the back of the property. Id. at 17, 28. When Szoka removed the existing septic tank, he found it to be lined with 2-4 inches of an unusual greasy, unidentified coating that had a smell similar to that of oil. DefiApp., Exh. H, pp. 12-13. The inside of the tank was scrubbed and flushed three times to remove the coating. Id. at 13-14, 16. The coating removed from tank was taken from the property. Id. at 14. H. Merkel asserts that no one told him about the unusual substance that was found in the septic system at the time, but B. Merkel remembers that Vail told him something about it. DeflApp., Exh. Q, pp. 56-57, 86; Exh. R, pp. 41-42. B. Merkel remembers that nothing said to him led him to believe that he should be concerned about what was found in the septic system. Def.App., Exh. R, pp. 42-43.

Szoka’s upgrade of the septic system included the creation of a leachfield. Sewerage plans approved by Ohio EPA, Pl. App., Exh. 15; Def.App. H, pp. 17-18. Effluent went from the building to a dozing tank, from which it was pumped to a sand filter. DeflApp. H, pp. 18. The effluent sank through the sand filter, then it was piped to a 1,000-foot leach bed north of the building. Id; PLApp., Exh. 15.

Installation of the new septic system may have involved the movement of large quantities of soil north of the building. According to Mark F. Deering (“Deer-ing”), a geologist for Sanborn, Head & Associates (“Sanborne”), “During the excavation of the area, the CVOCs that were in the soils were moved and dispersed.” Affidavit of Deering, PLApp., Exh. 18, p. 2; see also photographs of septic installation, PLApp., Exh. 17. Deering is also of the opinion that “the movement of the CVOC contaminated soils volatized some of the contaminants and emitted them into the ambient air.” Affidavit of Deering, Pl. App., Exh. 18, p. 2. The distribution of CVOCs in the soil loosely corresponds with the area in which the leachfield was created. Cf. area indicated as leachfield in Pl. App., Exh. 15 to Table 1: “Concentration of CVOCs in Soil Samples” (“Table 1”), PLApp., Exh. 16. This area also partly overlaps the outside drum storage area, cf. PLApp., Exh. 16, Table 1 to description of the outside drum storage area at DeflApp., Exh. Q, p. 29, and it begins immediately downgradient (i.e. “downstream” of the flow of underground water) from the original septic system. Cf. the location of the original septic system in PLApp., Exh. 1, p. 3 and in Defendants, Albatross Ltd., Benjamin Merkel and Henry Merkel’s Brief in Opposition to Plaintiffs Motion for Partial Summary Judgment (Docket # 100), Exh. DD to PLApp., Exh. 16, Table 1; see Pl. App., Exh. 8, p. 20 regarding the generally southwest flow of underground water at the site.

S. Oil contamination

On January 4, 1988 Bob’s Beverage discovered fuel oil or diesel oil coming from a water spigot at the “Hitchin’ Post.” Def. App., Exh. F, pp. 13-14, 134. The source of the fuel leak which caused this contamination has not been positively identified, but Bob Ullman, Inc. (renamed Ullman Oil on November 12, 1988) took responsibility for the contamination. Id. at 135-37. Ull-man Oil contacted the Ohio EPA and its insurance company regarding the problem. By March 9, 1988 an oil recovery system had been put in place to clean up the contamination. Id. at 136. The Ohio Bureau of Underground Storage Tanks (“BUST”) approved discontinuance of the primary cleanup in December 1991. Feasibility Study Report, PLApp., Exh. 8., p. 4. Ullman Oil does have some ongoing responsibility to BUST to clean up this contamination, and there has been further bailing and pumping of wells to remove contaminants. Id.; DeflApp., Exh. F, pp. 159-60.

D. Ownership of the site by Bob’s Beverage

Albatross sold the site to Bob’s Beverage in May 1988. Plaintiffs Motion for Partial Summary Judgment, p. 6. Bob’s Beverage did not conduct an environmental assessment of the site before buying it, although it knew of the fuel oil contamination in the subsurface of the site. Id. at 6-7; Def.App., Exh. F, pp. 22-23. Bob Ull-man, Inc. became the operator of the site in July 1988. DelApp. Exh. R, p. 6.

Albatross did not warrant the property to be free from contamination when it sold the site. Def.App., Exh. F, pp. 85-86, 94-95. H. Merkel avers that Albatross could not warrant that there was no environmental waste on the site because it “could not vouch for what had been done to the property before we had it.” Id. at 86. B. Merkel asserts that the partners in Albatross had no knowledge of what business had been conducted on the site before they bought it, other than what could be deduced from the condition of the property. Def.App., Exh. R, pp. 14-15, 56.

E. Contamination by CVOCs

In November 1988 Bob’s Beverage discovered CVOCs in groundwater samples taken from monitoring wells at the site. Pl.App., Exh. 8, p. 4. Investigators first detected CVOCs above the Maximum Contaminant Level (MCL) set by the Federal Environmental Protection Agency (“Federal EPA”) in monitoring well MW-7 immediately north of the building. PLApp., Exh. 8, p. 4; Exh. 16, Table 2: “Concentrations of CVOCs and BTEX Compounds in Shallow Groundwater” (“Table 2”). Analyses showed that “concentrations of 1.1-dichloroethene, tetrachloroethene, 1.1.1-trichloroethane, and trichloroethene routinely exceeded MCLs for samples analyzed between 1988 and 1991.” PLApp., Exh. 8, p. 4 (abbreviations deleted). Investigators detected “several CVOCs,” including 1,1-dichloroethene above the M.C.L. § in recovery wells RW-2 and RW-3 and 1,1,1-trichloroethane above the M.C.L. § in well RW-3. Id. Wells RW-2 and RW-3 were respectively west and south of the building. PLApp., Exh. 16, Table 2. Beginning in 1988 investigators also detected CVOCs below MCLs in one monitoring well directly south of the building on the site (MW-10), in three monitoring wells south of the building across East Washington Street (MW-4, MW-8, MW-9), and in one monitoring well west of the building and west of the Hitchin’ Post at the Nasady residence (MW-5). PLApp., Exh. 8, p. 5; Exh. 16, Table 2.

Investigators sampled four private water supplies west, south, and east of the building in November 1991. PLApp., Exh. 8, p. 5. They detected 1,1-dichloroethene, 1,1-dichloroethane, and tuolene below MCLs in the Konst water supply directly south and across the street from the building. Id. In October 1994 they detected CVOCs in the Auburn Center Plaza water supply east of the building. Id. at 20. The level of CVOCs in both water supplies has increased over time. Id.

Bob’s Beverage reported the detection of CVOCs in 1989 through 1991 to the BUST as part of its remediation of petroleum products contamination. Id. Bob’s Beverage notified the Ohio EPA of the detection of CVOCs on June 17, 1992. Pl. App., Exh. 8, p. 5. Bob’s Beverage entered into a consent order with Ohio EPA, effective September 13, 1994, requiring it to complete a remedial investigation and a feasibility study regarding CVOC contamination. Id. at 5; Administrative Order on Consent, PLApp., Exh. 19. Despite entering into a consent order, both Bob’s Beverage and Ullman Oil aver that they have never “used, stored, treated, or disposed of chlorinated solvents at 9810 or 9812 East Washington Street property.” Plaintiffs Motion for Partial Summary Judgment, p. 7.

Ullman Oil undertook the remedial investigation and feasibility study on behalf of Bob’s Beverage. PLMot., p. 17. San-born was retained to conduct the remedial investigation and feasibility study required by the consent order. PLApp., Exh. 9, p. 1.

Sanborn held a public meeting in conjunction with the Ohio EPA on June 5, 1995 to provide information regarding the status, plans, and objectives of the remedial investigation to the public, in accordance with the Remedial Investigation Workplan. Id. at 6. Sanborn also set up and has maintained a repository of documents related to the remedial investigation at the Bainbridge Branch of the Geauga County Library. Id.

Sanborn discovered 1,1,1-trichloroeth-ane and trichloroethylene on the site. PI. App., Exh. 8, p. 2. It also discovered 1,1-dichloroethylene, a breakdown product of trichloroethylene, and 1,1-dichloroethane, a breakdown product of 1,1,1-triehloroeth-ane, in water wells east and south of the site. Id. The investigation identified an area north of the Ullman Oil building as the source of these contaminants. Id. Investigators found that “[gjroundwater quality data indicate clearly that CVOCs have migrated from the identified source area at the site. These contaminants will continue to migrate in groundwater, impacting water quality conditions at and in the vicinity of the Site.” Id. Investigators are of the opinion that the CVOCs at the site “have migrated from the surface or the shallow subsurface and through the soil to the groundwater.... ” Deposition of Deering, Def.App., Exh. S, p. 165. More particularly, the investigators found that “these chemicals could have been released to the ground by leakage or spillage from drums, discharge to the subsurface via septic system components (drag-out of solvents from parts cleaning, for example), or direct discharge to the ground surface.” PLApp., Exh. 9, p. 4.

Sanborn submitted its Remedial Investigation Report to the Ohio EPA in June 1996. Id. at 1. The Ohio EPA approved that report on October 3, 1996. Letter of October 3, 1996 from Ohio EPA to Deer-ing, PLApp., Exh. 20. Sanborn and the Ohio EPA agreed on the basis of that report “that it was appropriate to focus the scope and approach of the [feasibility study] to a review of technologies related to groundwater extraction and treatment and source area remedy.” PLApp., Exh. 9, p. 1. Sanborn completed the feasibility study in accordance with the consent order and according to evaluation criteria included in the National Contingency Plan (NCP). Id. Sanborn submitted the Feasibility Study Report to the Ohio EPA in July 1988, and that report is currently under Agency review. Id. at 1-2; see also Feasibility Study Report, PLApp., Exh. 16, pp. 25-26.

Ullman Oil claims to have incurred $441,622.85 in expenses associated with remedial action in response to the contamination. Summary of Expenses Associated with Remedial Action for Ullman Oil, Inc., Pl.App., Exh. 24. It asserts that none of these expenses is related to the clean-up of the petroleum contamination discovered in 1988. DefApp., Exh. F, pp. 183-85.

II. Summary judgment standard

All parties move for partial or total summary judgment on the complaint. Summary judgment is appropriate only when there is no genuine issue of material fact and the movant is entitled to judgment as a matter of law. Fed.R.Civ.P. 56(c); Celotex Corp. v. Catrett, 477 U.S. 317, 106 S.Ct. 2548, 91 L.Ed.2d 265 (1986). The moving party must demonstrate through reference to pleadings and discovery the absence of a genuine issue of material fact. Id. at 323, 106 S.Ct. 2548. The nonmoving party must then show the existence of a material fact which must be tried. Id. at 324, 106 S.Ct. 2548.

When evaluating a motion for summary judgment, “the inferences to be drawn from the underlying facts ... must be viewed in the light most favorable to ... the party opposing the motion....” United States v. Diebold, Inc., 369 U.S. 654, 655, 82 S.Ct. 993, 8 L.Ed.2d 176 (1962); see also Poller v. Columbia Broad. Sys., Inc., 368 U.S. 464, 473, 82 S.Ct. 486, 7 L.Ed.2d 458 (1962); Aetna Ins. Co. v. Loveland Gas & Elec. Co., 12 Ohio Misc. 230, 369 F.2d 648 (6th Cir.1966). This includes taking the nonmoving party’s un-contradicted allegations as true and giving the benefit of the doubt to the nonmoving party’s assertions when they conflict with those of the movant. Bishop v. Wood, 426 U.S. 341, 96 S.Ct. 2074, 48 L.Ed.2d 684 (1976); Bosely v. City of Euclid, 496 F.2d 193, 197 (6th Cir.1974).

The court’s treatment of facts and inferences in a light favorable to the nonmoving party does not relieve that party of its obligation “to go beyond the pleadings” to oppose an otherwise properly supported motion for summary judgment under Rule 56(e). See Celotex, 477 U.S. at 324, 106 S.Ct. 2548. The nonmoving party may oppose a proper summary judgment motion “by any of the kinds of evidentiary material listed in Rule 56(c), except the mere pleadings themselves ...,” id, or by any other evidentiary material admissible at trial. Horta v. Sullivan, 4 F.3d 2, 8 (1st Cir.1993); see also ChaRles Alan Weight & Arthur R. Miller, Federal Praotioe AND PROCEDURE, 10A, § 2721 (1998). A scintilla of evidence in favor of the nonmoving party is not sufficient. There must be enough evidence that a reasonable jury could find for the nonmoving party. Street v. J.C. Bradford & Co., 886 F.2d 1472, 1477 (6th Cir.1989).

III. Plaintiffs’ motion for summary judgment

A. Claim under 12 U.S.C. § 9607(a)

Plaintiffs Bob’s Beverage and Ullman Oil move for summary judgment as to certain issues implicated in a cause of action under 42 U.S.C. § 9607(a). Defendants Acme and Bares respond that plaintiffs have no cause of action under § 9607(a) because they are potentially responsible parties (“PRPs”) who only may bring a cause of action against defendants under 42 U.S.C. § 9613(f). This argument is well taken.

1. The two causes of action

CERCLA provides causes of action for private parties seeking to recover the costs of remediating a hazardous waste site from parties who share responsibility for the disposal of waste at the site. Title 42 U.S.C. § 9607(a) authorizes a party who has incurred costs in removing contamination from a site to recover these response costs from PRPs. Section 9607(a) provides in relevant part:

Notwithstanding any other provision or rule of law, and subject only to the defenses set forth in subsection (b) of this section'—

(1) the owner and operator of a vessel or a facility, [and]

(2) any person who at the time of disposal of any hazardous substance owned or operated any facility at which such hazardous substances were disposed of ... shall be liable for ... (B) any ... necessary costs or response incurred by any other person consistent with the national contingency plan....

Title 42 U.S.C. § 9613(f)(1) also provides a cause of action by which a party who has incurred response costs may seek reimbursement from responsible parties:

Any person may seek contribution from any other person who is liable or potentially liable under section 9607(a) of this title, during or following any civil action under section 9606 of this title or under section 9607(a) of this title. Such claims shall be brought in accordance with this section and the Federal Rules of Civil Procedure, and shall be governed by Federal law. In resolving contribution claims, the court may allocate response costs among liable parties using such equitable factors as the court determines are appropriate.

The two causes of action differ in important respects. Liability under § 9607(a) is strict and usually joint and several. Centerior Serv. Co. v. Acme Scrap Iron & Metal Corp., 153 F.3d 344, 348 (6th Cir.1998). Damages will be apportioned according to fault only if a defendant can affirmatively demonstrate that the harm suffered is divisible into discrete, lesser harms whose causes are attributable to particular parties. Id.; United States v. Township of Brighton, 153 F.3d 307 (6th Cir.1998).

Liability under § 9613 is equitable and several. Centerior, 153 F.3d at 348. Plaintiff has the burden of establishing each party’s equitable share of response costs. Id.

2. PRPs, the third party defense, and availability of action under § 9607(a)

The Sixth Circuit has found generally that “parties who are themselves PRPs, potentially hable under CERCLA and compelled to initiate a hazardous waste site cleanup, may not bring an action for joint and several cost recovery, but are limited to actions for contribution governed by the mechanisms set forth in CERCLA § 113(f).” Id. at 356. The Sixth Circuit has not found, however, that an “innocent” PRP who has not contributed to site contamination may not seek joint and several cost recovery under § 9607(a). See Centerior, 153 F.3d at 351, n. 10.

An innocent private party may bring an action under § 9607(a) even if the party is a PRP: “One example of an innocent private party is ... one who, although otherwise potentially responsible for paying necessary clean-up costs, ‘can successfully assert one of the affirmative defenses enumerated in § 9607(b).’” Dartron Corp. v. Uniroyal Chem. Co., Inc., 917 F.Supp. 1173, 1182 (N.D.Ohio 1996) (quoting Kaufman & Broad-South Bay v. Unisys Corp., 868 F.Supp. 1212, 1214 (N.D.Cal.1994)). There are four defenses enumerated in § 9607(b): the contamination was caused 1) by an act of God, 2) by an act of war, 3) by an act or omission of a third party who is not the employee or agent of the party asserting the defense and was not acting in connection with a contractual relationship with that party (the “third-party defense”), or 4) by some combination of the preceding three.

Bob’s Beverage and Ullman Oil are PRPs because they are current owner or operator of a waste facility. Centerior, 153 F.3d. at 347 n. 8; see 42 U.S.C. § 9607(a)(1). They claim that they are innocent PRPs and assert the third-party defense.

The third-party defense requires the party raising it to show by a preponderance of the evidence that (1) some other party was the sole cause of the release of hazardous substances and the damages caused by the release; (2) the party responsible for the release did not cause the release in connection with a contractual, employment, or agency relationship with the defendant; (3) the defendant took precautions against foreseeable acts or omissions of any third party and against the consequences that could foreseeably result from those acts or omissions; and (4) the defendant “exercised due care with respect to the hazardous substance concerned, taking into consideration the characteristics of such hazardous substance, in light of all relevant facts and circumstances.... ” Title 42 U.S.C. § 9607(b)(3)(a) — (b); Westfarm Assocls Ltd. Partnership v. Washington Suburban Sanitary Comm’n, 66 F.3d 669 (4th Cir.1995). This exception to liability for PRPs is exclusive and must be rigorously applied: “This explicitly drafted exception ... signals Congress’ intent to impose liability on landowners who cannot satisfy its express requirements.” Monsanto, 858 F.2d at 168 n. 14.

3. Plaintiffs and the third party defense

a. Third party sole cause of the release

Plaintiffs have offered sufficient evidence to support their contention that some other party was the sole cause of the release of hazardous substances and the damages caused by the release. The evidence shows that CVOCs were originally deposited in a particular area at the site. PLApp., Exh. 16, Table 1. The CVOCs detected include 1,1,1-trichloroethane, trichloroethylene, and CVOCs which are the products of the breakdown of 1,1,1-trichlo-roethane and trichloroethylene. PLApp., Exh. 8, p. 2. Defendants Acme and Bares admit to having used 1,1,1-trichloroethane and trichloroethylene at the site. PLApp., Exh. 2, p. 4; Def.App., Exh. K, pp. 79-80, 83-86. Sanborn’s report asserts that “Ull-man Oil has never used chlorinated solvents for any of its operations at the site.” PLApp., Exh. 8, “Executive Summary.” The septic system which may have been a source of contamination was replaced and the barrels which may have contained CVOCs were removed before Bob’s Beverage bought the site. These facts are sufficient to prove by a preponderance of the evidence that some party other than Bob’s Beverage/Ullman Oil was the sole cause of the release of hazardous substances and the resulting damage.

b. Release not in connection with a contractual relationship

The facts presented are sufficient to show that the party responsible for the release did not cause the release in connection with a contractual, employment, or agency relationship with the plaintiffs. The phrase “in connection with a contractual relationship”

requires more than the mere existence, of a contractual relationship between the owner of land on which hazardous substances are or have been disposed of and a third party whose act or omission was the sole cause of the release or threatened release of such hazardous substances into the environment, for the landowner to be barred from raising the third-party defense provided for in that section. In order for the landowner to be barred from raising the third-party defense under such circumstances, the contract between the landowner and the third party must either relate to the hazardous substances or allow the landowner to exert some element of control over the third party’s activities.

Westwood Pharms., Inc. v. National Fuel Gas Distrib. Corp., 964 F.2d 85, 91-92 (2nd Cir.1992); see also State of New York v. Lashins Arcade Co., 91 F.3d 353, 360-61 (2nd Cir.1996). There must “be some relationship between the disposal/releasing activity and the contract with the defendant for a defendant to be barred from raising the third-party defense.” Westwood, 964 F.2d at 88. Any other interpretation “would render the language ‘in connection with’ superfluous, a result generally at odds with an accepted principle of statutory construction.” Id.

The only defendant with whom any plaintiff had a contractual relationship was Albatross. Bob’s Beverage entered into a contractual relationship with Albatross when it bought the site from Albatross. The contractual relationship between Bob’s Beverage and Albatross did not relate to the hazardous substances at issue or allow Bob’s Beverage to exert some element of control over Albatross’ activities related to the release of contaminants. Bob’s Beverage may not be disqualified, therefore, from raising the third-party defense because of its contractual relationship with Albatross.

c. Precautions against foreseeable acts or omissions of third party

The third element, that the party raising the defense “took precautions against foreseeable acts or omissions of any such third party and the consequences that could foreseeably result from such acts or omissions ...is not applicable to the instant case because the contamination took place before plaintiffs bought the site. The requirement that the party raising the defense has taken precautions against foreseeable acts or omissions of a third party “does not prevent a subsequent purchaser after contamination has occurred from claiming the defense, but only comes into play after the landowner acquires the property.” H.R.Conf.Rep. No. 962 (1986), reprinted in 1986 U.S.C.C.A.N. 3276, 1986 WL 31924, at 12 (Legis.Hist.).

d. Exercise of due care with respect to hazardous substance

Bob’s Beverage has not offered sufficient evidence that it “exercised due care with respect to the hazardous substance concerned, taking into consideration the characteristics of such hazardous substance, in light of all relevant facts and circumstances.... ” The statute does not define what “due care” means in this context. The House Report which accompanied CERCLA indicates that a party seeking to raise the defense “must demonstrate that he took all precautions with respect to the particular waste that a similarly situated reasonable and prudent person would have taken in light of all relevant-facts and circumstances.” H.R.Rep. No. 1016, at 34 (1980), reprinted in 1980 U.S.C.C.A.N. 6119, 6137. “Due care” does not “impose a duty on a purchaser of land to investigate prior to purchase, in order to determine whether there is pollution on the land caused by someone with whom the purchaser is not in contractual privity.” Lashins, 91 F.3d at 361 (quoting HRW Systems, Inc. v. Washington Gas Light Co., 823 F.Supp. 318, 349 (D.Md.1993)). “Due care” does require a party, however, to take “those steps necessary to protect the public from a health or environmental threat.” Lashins, 91 F.3d at 361 (quoting H.R.Conf.Rep. No. 962 (1986), reprinted in 1986 U.S.C.C.A.N. 3276, 1986 WL 31924, at 12 (Legis.Hist.), and United States v. A & N Cleaners & Launderers, Inc., 854 F.Supp. 229, 238 (S.D.N.Y.1994)).

In the instant case Bob’s Beverage first detected CVOCs in on-site groundwater well samples taken as part of its remediation of petroleum product contamination in November 1988. In that year investigators found CVOCs above the M.C.L. § in three wells north, west, and south of the building. One of those wells “routinely exceeded MCLs [for CVOCs] for samples analyzed between 1988 and 1991.” PI. App., Exh. 8, p. 4. Investigators also detected CVOCs below MCLs in one monitoring well directly south of the building (MW-10), in three monitoring wells south of the building across East Washington Street (MW-4, MW-8, MW-9), and in one monitoring well west of the building and west of the Hitchin’ Post at the Nasady residence (MW-5) in 1988. Pl.App., Exh. 8, p. 5; Exh. 16, Table 2. In November 1991 investigators detected CVOCs below the MCLs in the Konst water supply directly south and across the street from the building. Id.

Bob’s Beverage reported the detection of CVOCs in reports made in 1989 through 1991 to the BUST as part of its remediation of petroleum products contamination. Id. BUST is a bureau of the State Fire Marshall, which is in turn a division of the Ohio Department of Commerce. See Business & Legal Reports, Inc., Environmental ComplianCe in Ohio, U-9 (1998). Ohio law charges the State Fire Marshall with supervising and regulating underground storage tanks and with taking action to correct petroleum releases. Ohio Rev. Code. §§ 3737.87 et seq. Neither the State Fire Marshall nor BUST has any authority to evaluate, correct, or supervise correction of a release of a non-petroleum contaminant unconnected with underground storage tanks.

Bob’s Beverage did not report the detection of CVOCs to the Federal EPA. It did not report the detection of CVOCs to the Ohio EPA until June 17, 1992. Pl.App., Exh. 8, p. 5. This report came more than two and a half years after detecting CVOCs above the MCLs at three locations on its own property and more than seven months after detecting CVOCs in the drinking supply of a neighbor. Bob’s Beverage failed to report the contamination more quickly even though, by its own account, many 55-gallon drums had been left outside, unattended on the property, which adjoined its own, for years. A reasonable jury could not conclude that Bob’s Beverage took “all precautions with respect to the particular waste that a similarly situated reasonable and prudent person would have taken in light of all relevant facts and circumstances.”

Because Bob’s Beverage has not offered sufficient evidence that it exercised due care with respect to the hazardous substance, it cannot claim to be an innocent landowner. Because it is a PRP who is not an innocent landowner, Bob’s Beverage cannot initiate a cause of action under 42 U.S.C. § 9607(a). If Bob’s Beverage has borne response costs related to the release of a hazardous substance, it must seek contribution under 42 U.S.C. § 9613(f).

Nor can Ullman Oil proceed as an innocent party under 42 U.S.C. § 9607(a). Ull-man Oil, as the operator of the site, is a PRP. 42 U.S.C. § 9607(a)(1). It too must prove itself to be an innocent PRP to avail itself of the cause of action provided at § 9607(a). But Ullman Oil’s claim to be an innocent PRP founders because the same persons who are the officers, directors, and owners of Bob’s Beverage are also the officers, directors, and owners of Ulman Oil. Def.App., Exh. F, pp. 20-22. If those persons are not innocent in their legal persona of Bob’s Beverage because they failed timely to report known CVOC contamination at the site to the proper authority, then they cannot be innocent in their legal persona of Ullman Oil. As either PRP they failed timely and properly to report known contamination and cannot now claim to have taken “all precautions with respect to the particular waste that a similarly situated reasonable and prudent person would have taken in light of all relevant facts and circumstances.”

The court need not make fine distinctions regarding the capacity in which the joint officers, directors, and shareholders of Bob’s Beverage and Ullman failed to act timely in addressing contamination at the site. Those parties themselves have blurred the capacities in which they addressed that contamination. Both Bob’s Beverage, as owner, and Ullman Oil, as operator, are potentially liable for response costs for dealing with the CVOCs found at the facility. See 42 U.S.C. § 9607(a)(1). Yet Ullman Oil has paid the entire cost of implementing the plan outlined in the consent decree entered into between Bob’s Beverage and the Ohio EPA. Answers to Defendants Albatross, Ltd. and Benjamin H. Merkel’s First Set of Interrogatories Propounded to Plaintiffs, Def.App., Exh. E, p. 6; PLApp., Exh.’s 19, 24. This does not reflect a punctilious observance of corporate forms.

For these reasons, if Ullman Oil has borne response costs related to the release of a hazardous substance, it must seek contribution under 42 U.S.C. § 9613(f).

B. Elements of a cause of action authorized by i2 U.S.C. § 9613(f)

An action under § 9613(f) allows a plaintiff to “seek contribution from any other person who is liable or potentially liable under [42 U.S.C. § 9607(a) ].” 42 U.S.C. § 9613(f)(1). Liability for contribution under § 9613(f) and available defenses to liability, therefore, are determined by § 9607(a). Centerior, 153 F.3d at 350.

There are four elements which a plaintiff must prove to establish a prima facie case for liability for response costs under § 9607(a): (1) the property at issue was a “facility” as defined by CERCLA; (2) there was a release or threatened release of a hazardous substance from the facility; (3) the release or threatened release caused plaintiffs to incur response costs that were necessary and consistent with the NCP; and (4) defendant was a person subject to liability under § 9607(a). Centerior, 153 F.3d at 347-48; City of Toledo v. Beazer Materials and Serv.’s, Inc., 923 F.Supp. 1001, 1002 (N.D.Ohio 1996).

Plaintiffs ask for summary judgment as to issues raised under 42 U.S.C. § 9607(a).

C. Summary judgment as to issues raised under § 9613(f)

1. Whether the properties at 9810 and 9812 East Washington Street and contiguous properties contaminated by CVOCs are a “facility”

Plaintiffs move for summary judgment on the issue of whether the properties at 9810 and 9812 East Washington Street and those contiguous properties contaminated by CVOCs are a “facility” as defined by CERCLA. The court concludes that they are.

Title 42 U.S.C. § 9601(9) defines a “facility” for purposes of CERCLA:

The term “facility” means (A) any building, structure, installation, equipment, pipe or pipeline (including any pipe into a sewer or publicly owned treatment works), well, pit, pond, lagoon, impoundment, ditch, landfill, storage container, motor vehicle, rolling stock, or aircraft, or (B) any site or area where a hazardous substance has been deposited, stored, disposed of, or placed, or otherwise come to be located....

Undisputed evidence shows that CVOCs have come to be located in the soil and groundwater of 9810 and 9812 East Washington Street and in the soil and groundwater of contiguous properties south and west of the site. Pl.App., Exh. 8, pp. 4, 5, 8; Exh. 16, Table 2. These CVOCs are hazardous substances. See infra, III.C.2.

Thus the properties at 9810 and 9812 East Washington Street and the contiguous properties south and west of the site fall squarely within the definition of “facility.”

2. Whether the CVOCs found at the site are hazardous substances.

Plaintiffs move for summary judgment on the issue of whether CVOCs detected at the facility are hazardous substances. The court concludes that they are.

Section 9601(14) defines “hazardous substance” as any substance designated pursuant to 42 U.S.C. § 6902 or any hazardous waste having the characteristics identified under or listed at 42 U.S.C. § 6921. Investigators have detected 1,1-dichloroethene, 1,1-dichloroethane, tetrachloroethene, 1,1,1-trichloroethane, and trichloroethene at the facility. PLApp., Exh. 8, pp. 4-5; Exh. 16, Table 2. Of these, 1,1-dichloroethane, tetrachloroeth-ene, 1,1,1-trichloroethane, and trichlo-roethene are listed by the Federal EPA at 40 C.F.R. § 302.4, pursuant to 42 U.S.C. § 6902, as being hazardous substances.

No genuine issue of material fact remains regarding this issue. The 1,1-di-chloroethane, tetrachloroethene, 1,1,1-tri-chloroethane, and trichloroethene found at the facility are hazardous substances.

3. Whether the defendants are “persons” for purposes of liability under § 9607(a)

Plaintiffs argue that defendants Bares, Acme, Albatross, B. Merkel, and H. Merk-el are “persons” for purposes of liability under § 9607(a). The court agrees.

Section 9607(a)(2) provides for liability for “any person who at the time of disposal of any hazardous substance owned or operated any facility at which such hazardous substances were disposed of....” Section 9601(21) defines “person” as “an individual, firm, corporation, association, partnership, consortium, joint venture, commercial entity, United States Government, State, municipality, commission, political subdivision of a State, or any interstate body.” Defendants are facially “persons” within the meaning of the statute. Bares, B. Merkel, and H. Merkel are individuals; Acme is a corporation; and Albatross is a partnership.

Acme argues that it is not a viable party to this litigation because the corporation has been dissolved and its assets sold. It contends that Acme no longer exists as a legal entity which might participate in the litigation. That argument is not well taken.

Common law abated all litigation to which a corporation was a party when the corporation dissolved. The life of a corporation may be prolonged by statute, however, for purposes of litigation. Chadwick v. Air Reduction Co., 5 Ohio Misc. 171, 239 F.Supp. 247, 250 (N.D.Ohio 1965) (citing 13 Ohio JURISPRUDENCE 2nd, Corporation, § 937). Ohio Rev.Code § 1701.88 provides:

(A) When a corporation is dissolved voluntarily, when the articles of a corporation have been canceled, or when the period of existence of the corporation specified in its articles has expired, the corporation shall cease to carry on business and shall do only such acts as are required to wind up its affairs, or to obtain reinstatement of the articles ... and for such purposes it shall continue as a corporation.

(B) Any claim existing or action or proceeding pending by or against the corporation or which would have accrued against it may be prosecuted to judgment, with right of appeal as in other cases....

Such a statute “extending the vitality of a dissolved corporation for purposes of suit are remedial in nature and should be given a liberal construction.” Chadwick, 239 F.Supp. at 251 (citing 16 A Fletcher Cyclopedia, Corporations § 8143); see also American Oak Leather v. Peck, 48 Ohio Op. 291, 296, 108 N.E.2d 179, 183 (1951).

Chadwick construed the meaning of Ohio Rev.Code § 1701.88 regarding causes of action which would have accrued against a corporate entity had it not dissolved:

Any claim existing (not yet sued upon) or action or proceeding (already commenced) pending by or against the (dissolved) corporation or (any claim not yet sued upon or action or proceeding) which would have accrued against it (had dissolution not occurred) may be prosecuted to judgment, with right of appeal as in other cases....

Chadwick, 239 F.Supp. at 251. Ohio courts are in accord with this position. In North Consultants, Inc. v. Jane Stimel-Givens the court observed that cancellation of a corporation’s charter

in no way represents a forfeiture of the corporation’s franchise. The cancellation represents no more than a suspension of the corporation’s right to do business. The corporation may continue to operate as is necessary in the winding-up process, and formal action in quo warranto is required to revoke its corporate charter. Moreover, even if a corporation is dissolved it may still be sued, and satisfaction or performance of any judgment obtained may be enforced against such corporation.

1985 WL 10281, at *3 (Ohio App. 10 Dist. May 14, 1985) (emphasis added) (citations omitted); see also Diversified Property Corp. v. Winters Nat’l Bank and Trust Co., 13 Ohio App.2d 190, 193, 234 N.E.2d 608, 610 (Ohio Ct.App.1967). Service upon a dissolved corporation may be accomplished “by delivering a copy to an officer, director, liquidator, or person having charge of its assets or, if no such person can be found, to the statutory agent.” Ohio Rev.Code § 1701.88(C). A judgment obtained against a dissolved corporation may be enforced “against the assets in the hands of the shareholders.” North Consultants, 1985 WL 10281 at *3; see also Kesselring Ford, Inc. v. Cann, 68 Ohio App.2d 131, 427 N.E.2d 785 (1980).

This court sees no reason why “dissolution” law should not be applied in the event of cancellation of a corporate charter. In the instant case, if a cause of action under CERCLA would have accrued against Acme had it not dissolved, then that cause of action may be prosecuted to judgment against the corporation. The cancellation of Acme’s corporate charter by the Ohio Secretary of State and' even the dissolution of the corporation consequent to “winding up” do not prevent a plaintiff with a valid cause of action against Acme from proceeding.

Thus the court concludes that all defendants are “persons” for purp