OPINION AND ORDER
Nоw before the Court are Defendants Blue Tee Corp. and Gold Fields Mining Corporation’s Motion for Partial Summary Judgment (Dkt.# 360) and Supplement to Blue Tee and Gold Field’s Motion for Partial Summary Judgment (Dkt.# 421).
I.
The Tar Creek Superfund Site (“Tar Creek”) is located in a 40 square mile area of northeastern Oklahoma that was historically the site of lead and zinc mining throughout the twentieth century. Tar Creek includes the communities of Picher, Cardin, Commerce, Quapaw, and North Miami in Ottawa County, Oklahoma. This case was brought on behalf of minor children residing in Picher and Cardin who allege that defendants’ mining activities contaminated their communities and caused children to suffer permanent neu-rocognitive disabilities due to lead poisoning. Plaintiffs claim that defendants’ actions constitute public and private nuisance under Oklahoma law, and plaintiffs seek injunctive relief, and actual and punitive damages. Defendants Blue Tee Corp. (“Blue Tee”) and Gold Fields Mining Corporation (“Gold Fields”) have filed a motion for partial summary judgment on plaintiffs’ claim for injunсtive relief and plaintiffs’ claims for public and private nuisance to the extent defendants’ activities occurred on restricted Quapaw lands.
Historical Mining Activities at Tar Creek
Early in the twentieth century, significant deposits of lead and zinc were discovered in southeastern Kansas and northeastern Oklahoma. Originally, mining activities were relatively small operations, but in the 1920s larger mining companies operated in the Tar Creek area. The defendants in this case are successor entities. Blue Tee is the successor to American Zinc, Lead & Smelting Company (“American Zinc”), and Gold Fields was formerly known as Tri-State Zinc, Inc. (“Tri-State”). Mining companies removed ore from the ground, stripped the ore of any valuable metals, and deposited waste material on the surface. Millions of tons of waste were left in Tar Creek in the form of chat piles and tailings ponds. Defendants assert that their companies were responsible for a minimal amount of the lead waste left behind in Tar Creek. 1
The mining companies generally did not own the land, but оbtained sub-surface leases or contracts to remove lead and zine ore from the ground. 2 Some of the land in northeastern Oklahoma was owned by members of the Quapaw Tribe in the form of allotments from the federal government, and this land was subject to federal regulation by the Department of Interior. In order to lease subsurface rights to restricted Quapaw land, mining companies had to execute a form lease approved by the Department of Interior and abide by certain federal regulations. Tri-State operated the White Mine from 1927 to 1930, and it later opened the Ottawa Mill in 1929 to *795 remill chat from the White Mine. In 1932, Tri-State obtained permission to remove tailings from restricted Quapaw land leased by the Eagle Picher Company (“Eagle Picher”) and remill the tailings at the Ottawa Mill. The Department of Interior required Tri-State to execute tailings re-treatment contracts to remove tailings from Quapaw land. The contracts provided that Tri-State could remill tailings removed from the property under the following conditions:
a. [Tri-State may] remove therefrom for the purpose of remilling and cleaning the tailings, chats and sands hereinafter described.
b. [Tri-State], by proper means of transportation to be by it selected, may haul and transport the chat and tailings in the [designated pile] to its mill or concentrating plant ... where such material may be mixed and co-mingled with other like material for purposes of extracting the metallic content thereof.
c. Tailings and other waste material resulting from said operation shall be allocated to each respective tract equal to the tonnage removed therefrom less concentrates extracted and first party agrees to store the same free of charge to the landowner with the right and privilege to the landowner to enter and remove the same.
d. Party of the second part ... shall so pile the tailings and other waste material on the mill site so as not to interfere with the mine operations on this land.
e. The right is reservеd in the Secretary of the Interior and to the Superintendent of the Quapaw Agency ... to inspect and check said operations at any and all reasonable times for the purpose of ascertaining whether the provisions of the Department of Interior regulations and the terms and provisions of this agreement are being complied with....
Dkt. # 360, Ex. 17, at 27. In 1935, TriState constructed the Sooner Mill for the purpose of expanding its remilling operations. The Sooner Mill was located in the northwest quarter of Section 16, T-29-N, R-23-E and the land consisted entirely of allotments owned by Quapaw Indians. After 1935, Tri-State entered additional tail-ings retreatment contracts with members of the Quapaw tribe. Between 1929 and 1947, Tri-State processed tailings from the following locations within Quapaw territory: (1) all of section 16, T-29-N, R-23-E; (2) NE/4 of section 21, T-29-N, R-23-E; (3) NE/4, NW/4 of section 21, T-29-N, R-23-E; (4) SE/4 of SE/4 of Section 17, T-29-N, R-23-E; (5) SE/4 of SW/4 of Section 17, T-29-N, R-23-E, (6) NW/4 of SW/4 of Section 17, T-29-N, R-23-E; and (7) SE/4 of NW/4 of Section 17, T-29-N, R-23-E. 3
American Zinc obtained subsurface leases in Ottawa County when it purchased the assets of the Nellie B. Company in October 1951, including the following leases on restricted Quapaw land: (1) the Thomas Buffalo Allotment — NW/4 and NE/4, SW/4 Section 28, T-29-N, R-23-E; (2) Buffalo Calf Allotment — NE/4, Section 28, T-29N, R-23-E; (3) Frank Buffalo Allotment — SE/4, and SE/4, SW/4 Section 28, T-29-N, R-23-E; (4) Mary Calf Allotment — W/2, SW/4 Section 28, T-29-N, R-23-E, E/2, SE/4, and NW/4, SE/4 Section 29, T-29-N, R-23-E. American Zinc also entered into an agreement with Eagle Picher to sell chat from the Eagle Picher *796 Central Mill. From 1951 to 1973, the re-milling operations of American Zinc-took place at the Barbara J and Rialto Mills.
Remilling produces tailings and chat, which are byproducts of the remilling process. Chat and tailings' were deposited on the surface. Defendants claim that they were contractually bound to leave the byproducts on the surface, but plaintiffs dispute this claim. Plaintiffs claim that mining companies left chat on the surface with the intent to extract more lead from the chat as remilling technology improved. They also claim that defendants’ contracts permitted them to store lead waste in a manner that would have prevented contamination from lead dust. Defendants claim that the Ottawa, Sooner, and the Barbara J and Rialto Mills were “subject to control by the Department of Interi- or.” 4 Dkt. # 360, at 22.
The Tar Creek Superfund Site
In 1983, the Environmental Protection Agency (“EPA”) placed approximately 40 square miles of northeastern Oklahoma on the National Priorities List (“NPL”), and the area was designated as the Tar Creek. The EPA notified mining companies that they could be held liable as potentially responsible parties (“PRPs”), and the EPA launched an investigation into the lead contamination found in the groundwater and surface contamination in the region. In 1991, the EPA entered a consent decree with several PRPs, including. Gold Fields and Blue Tee, requiring payment of $1,273,000 for the investigation and remediation of groundwater and surface water in Tar Creek. Subsequently, in 1993, the Indian Health Service conducted a study of children in Ottawa County, and found that 35% of children had blood lead levels exceeding the Center for Disease Control (“CDC”) minimum level of concern. 5 The EPA acknowledged as early as 1994 that many children in- Tar Creek had elevated blood lead levels, and it determined that additional investigation was necessary.
In September 1994, the EPA requested additional information from PRPs regarding the sources and cause of lead- contamination. Specifically, the EPA requested:
information relating to the identification, nature, and quantity of materials which have been generated, produced, treated, stored, or disposed at the Site or transported to the Site; information relating to the nature or extent of the release or threatened release of hazardous substances or pollutants or contaminants at or from the Site; and information relating to the ability of certain persons to pay for or to perform cleanup activities at the Site.
Dkt. # 361, Ex. 7, at 1. The EPA notified Blue Tee and Gold- Fields in August 1995 that it was planning soil remediation at Tar Creek, and asked whether the mining companies were willing to enter an agreement with the EPA. Blue Tee and Gold Fields refused to cooperate with the EPA’s cleanup efforts. 6 The EPA’s initial remed *797 iation efforts focused on soil removal near selected high access areas but, on March 21, 1996, the EPA expanded its activities to include soil remediation near residential homes. The EPA renewed its “invitation” to the defendants to assist with the costs of soil remediation, but the EPA admitted that it did not have any new evidence linking Blue Tee or Gold Fields to the lead contamination in Tar Creek.
The EPA formally began removal actions in June 1996. Since that time, the EPA’s activities can be broken four separate operable units of remedial action: (1) OU1 — monitoring of surface water and acid mine water discharges, and plugging wells to prevent additional contamination; (2) OU2 — soil sampling and remediation of residential areas; (3) OU3 — emergency removal action of soil from Eagle Picher laboratory; and (4) OU4 — RI/FS by the EPA, Blue Tee, and Gold Fields to determine feasible method to remove chat piles from Tar Creek region. 7 The EPA’s remediation efforts at Tar Creek are still in progress.
Community Health Action and Monitoring Program (“CHAMP”)
In 1996, Blue Tee and Gold Fields, along with other mining companies, established the CHAMP program to identify causеs of lead poisoning in Tar Creek. Defendants hired the University of Oklahoma Health Sciences Center to conduct research and report on its findings. The final work plan for CHAMP outlines the goals of the program:
The goal of CHAMP is to identify modifiable causes of elevated blood lead levels and reduce lead exposure in children and pregnant women. CHAMP provides community education on lead health issues and strategies for reducing children’s and pregnant women’s lead exposure. CHAMP includes a one-year blood monitoring program of children and pregnant women to assess lead exposure in the communities and identify those individuals who should be targeted for reduction in lead exposure and for case management. Individually tailored educational guidance will be provided to pregnant women and families of children with high blood lead levels and to those who are identified at high risk of exposure based on a survey questionnaire. A thorough environmental assessment of soil, dust, and paint will also be conducted on the homes of all children and pregnant women with elevated blood lead levels and on a random sample of homes of those without elevated blood lead levels. In addition, environmental abatement of dust and paint lead sources will be conducted as necessary.
Dkt. # 421, Ex. C, at 1. Defendants asked the EPA to delay soil remediation work until the completion of CHAMP, but the EPA refused to reschedule soil removal actions. 8
When CHAMP researchers completed their initial blood testing, they found that 38.3% of children in Picher and 62.5% of *798 children in Cardin had a lead blood level in excess of the minimum level recommended for action by the CDC. The program sponsors requested copies of the data and also contacted researchers to schedule a meeting. CHAMP’s principal investigator, Lorraine Malcoe, Ph.D., felt that direct contact with sponsors would violate professional ethics, and she refused to schedule to a meeting to discuss the results or the causes of lead poisoning suspected by researchers. She stated that program sponsors asked her to use her influence with families in Tar Creek to delay the EPA’s cleanup and, when she refused, the sponsors threatened to pull funding for CHAMP. Plaintiffs characterize the CHAMP program as an attempt to buy research proving that chat piles and tail-ings ponds were not the cause of lead contamination in Tar Creek. Defendants respond that they were simply asking to be notified of the results of research they funded, and they did not attempt to exert any improper influence over the independent judgment of CHAMP researchers.
CHAMP sponsors renewed their request to the EPA to delay soil remediation work for at least five months until the researchers could evaluate all of the CHAMP data. The EPA rejected the mining companies’ request to stop soil remediation at CHAMP homes. Although the EPA did not discourage the continuation ■ of CHAMP, it reiterated its position that CHAMP was not a substitute for the EPA’s cleanup efforts. The mining companies also argued that remediation could adversely affect the CHAMP study. However, the EPA was explicit that “the EPA does not believe that more data is needed to determine whether the Site requires remediation under Superfund.” Dkt. # 437, Ex. 121, at 2. Given the immediate threat of lead poisoning, the EPA believed that delaying soil remediation while investigating sources of lead contamination, other than chat piles and tailings ponds, made little sense. Although the EPA would not delay its work because of CHAMP, the EPA’s correspondence suggests that it viewed CHAMP as a useful supplemental activity, especially to reduce the risk of lead poisoning at homes until soil remediation was completed.
CHAMP was plagued by tensions between researchers and sponsors. Dr. Mal-coe felt that the mining companies were asking her not to disclose research results to state and federal agencies, because the results were harmful to the public perception of CHAMP sponsors. She admits that the educational aims of the program provided a significant benеfit to the community, even though the EPA could not take full advantage of CHAMP research. Plaintiffs have alleged that defendants intended to buy results through CHAMP to influence the EPA’s decision to impose cleanup costs on PRPs. They also claim that defendants intentionally disregarded CHAMP’s findings and delayed the EPA’s cleanup of Tar Creek, even though defendants knew of the potential harm to children if remediation did not occur quickly. Defendants deny these allegations, and characterize CHAMP as an independent research program designed to assist the residents of Tar Creek through education and by prioritizing cleanup.
II.
Summary judgment pursuant to Fed.R.Civ.P. 56 is appropriate where there is no genuine issue of material fact and the moving party is entitled to judgment as a matter of law.
Celotex Corp. v. Catrett,
“When the moving party has carried its burden under Rule 56(c), its opponent must do more than simply show that there is some metaphysical doubt as to the material facts.... Where the record taken as a whole could not lead a rational trier of fact to find for the non-moving party, there is no ‘genuine issue for trial.’”
Matsushita Elec. Indus. Co. v. Zenith Radio Corp.,
III.
Defendants argue that summary judgment should be granted for them on plaintiffs’ claim for injunctive relief (abatement of the nuisance), because the Court can not order abatement in this case. Defendants raise three separate arguments on this issue: (1) under common law, the Court can not order defendants to remove chat piles when they do not own the land or the chat piles; (2) an order for abatement would conflict with the federal remedial scheme under the Comprehensive Environmental Response, Compensation, and Liability Act, 42 U.S.C. § 9601 et seq. (“CERCLA”); and (3) the Court should invoke the doctrine of primary jurisdiction to prevent interference with an on-going administrative process.
A.
Defendants claim that the Court does not have the authority to order abatement, because defendants do not own the chat piles or the land where the chat piles are located. Plaintiffs respond that Oklahoma law authorizes the Court to order abatement against defendants, even though they do not currently own the land or the chat piles. Plaintiffs propose that the Court could order injunctive relief, but stay its order until the landowners are joined as parties.
Oklahoma law provides a common law and statutory claim for private nuisance, and plaintiffs make claims under both theories.
See Nichols v. Mid-Continent Pipe Line Co.,
A nuisance consists in unlawfully doing an act, or omitting to perform a duty, which act or omission either:
*800 First. Annoys, injures or endangers the comfort, repose, health, or safety of others; or
Second. Offends decency; or
Third. Unlawfully interferes with, obstructs or tends to obstruct, or renders dangerous for passage, any lake or navigable river, stream, canal or basin, or аny public park, square, street or highway; or
Fourth. In any way renders other persons insecure in life, or in the use of property, provided, this section shall not apply to preexisting agricultural activities.
Okla. Stat. tit. 50, § 1. Common law nuisance is defined more broadly as the “unwarrantable, unreasonable or unlawful use by a person of his own property to the injury of another.”
Lyons v. McKay,
Both parties rely on
Union Texas Petroleum Corp. v. Jackson,
This case is not particularly helpful in determining the limits of this Court’s authority to order abatement. The OCC was given express statutory authority to order corrective action against any “party responsible for the control of any salt water, crude oil or other deleterious substances.” Okla. Stat. tit. 29, § 7-401. The Oklahoma Supreme Court stated that none of the parties contested the OCC’s authority to order abatement against all of the defendants, and the authority of the OCC was not challenged on appeal.
Union Texas
*801
Petroleum,
Plaintiffs cite two cases from other states that have adopted a firm rule that any party that causes, creates, or maintains a nuisance can be ordered to abate the alleged nuisance.
Gray v. Westinghouse Elec. Corp.,
Although Oklahoma law permits a court to award damages against a defendant that does not control or own property, there is no clear law defining whether a court has the equitable authority to order abatement under these circumstances, nor does this Court need to predict what the Oklahoma Supreme Court would rule. Defendants have presented alternate arguments on the issue of injunctive relief, and the Court will consider whether federal law permits plaintiffs to proceed with their claims for abatement or if plaintiffs’ claims for abatement should be stayed under the dоctrine of primary jurisdiction.
B.
Defendants assert that they would be required to violate CERCLA if the Court were to order abatement in this case. Plaintiffs respond that CERCLA does not limit the Court’s authority to order abatement under a state law nuisance claim. Defendants rely on 42 U.S.C. § 9622(e)(6), which provides:
When either the President, or a potentially responsible party pursuant to an administrative order or consent decree under this chapter, has initiated a remedial investigation and feasibility study for a particular facility under this chapter, no potentially responsible party may undertake any remedial action at the facility unless such remedial action has been authorized by the President.
The parties do not dispute that the EPA has undertaken a remedial investigation at the Tar Creek site, and that the EPA is currently remediating residential yards. Defendants are asking the Court to find that section 9622 preempts the state law remedy of abatement, because the state law remedy comes into direct conflict with federal legislаtion. 10
*802
CERCLA is a comprehensive federal regulatory scheme that provides a regulatory process for cleaning up hazardous waste sites with-,the goal of restoring the environment.
New Mexico,
However, CERCLA does not preempt all state regulation regarding the management of hazardous substances within the state.
Bedford Affiliates v. Sills,
Defendants’ argument that section 9622(e)(6) precludes the Court from ordering abatement is misplaced, because it takes the statutory language out of context and distorts the meaning of the statute. The statutory language prevents PRPs from undertaking remedial action on their own initiative, in part, to рrevent PRPs from asserting a contribution claim for cleanup costs not authorized by the EPA.
Allied Corp. v. Acme Solvents Reclaiming, Inc.,
C.
Defendants request that the Court dismiss plaintiffs’ claim for injunctive relief under the doctrine of primary jurisdiction. They argue that the Court should defer to the EPA, because the EPA has substantial expertise remediating environmental hazards. Plaintiffs respond that, even if the Court invokes primary jurisdiction, the proper remedy is to stay their claims for injunctive relief.
The Supreme Court has recognized that there are circumstances when courts should avoid interference with an ongoing administrative process. Primary jurisdiction applies “where a claim is originally cognizable in the courts, and comes into play whenever enforcement of the claim requires resolution of issues which, under a regulatory scheme, have been placed within the special competence of an administrative body.”
United States v. Western Pacific Railroad Co.,
Both parties rely on
Schwartzman, Inc. v. Atchison, Topeka & Santa Fe Railway,
First, the factual issues that will have to be resolved to craft an order for injunctive relief are complex, and involve matters best left to the EPA for resolution. In order to grant injunctive relief, the Court would have tо authorize an investigation to determine the most reasonable method for abating the alleged nuisance caused by chat piles. Contrary to plaintiffs’ assertions, an order for abatement would not be as simple as ordering defendants to remove the chat piles once the EPA has completed its investigation. Although it would not be impossible for the Court to craft an appropriate order, it would certainly require help from outside sources. Plaintiffs argue that Oklahoma courts have frequently exercised their authority to order abatement in complex cases. Howev *804 er, the types of factual issues raised in this case are ordinarily left to the EPA for resolution, and the Court would likely be duplicating the investigation that has been underway since 1982. This factor favors abstention until the EPA resolves its investigation of Tar Creek.
Second, defendants would almost certainly be subject to conflicting orders from the Court and the EPA if the Court were to grant plaintiffs’ claims for injunctive relief at this time. The proper balance of judicial efficiency and administrative expertise in a specialized area such as environmental regulation favors abstention under this factor.
See Far East Conference v. United States,
Third, both parties admit that EPA has initiated an investigation of Tar Creek, and remediation is ongoing. Plaintiffs’ primary argument as to this factor was that Doe Run was not participating in remediation, but that issue is now moot.
12
The EPA has been actively working at Tar Creek since 1982, and has instituted at least four separate operable units of remedial action. This factor strongly favors the invocation of primary jurisdiction.
Loggerhead Turtle v. County Council of Volusia County, Florida,
Fourth, the EPA has conducted extensive investigatory and remedial work at Tar Creek, and is currently engaged in large scаle soil remediation efforts. Plaintiffs are understandably frustrated that Tar Creek has been listed as a Superfund site for over 20 years, and much work remains to be done. They cite one case criticizing the EPA in similar circumstances,
Davies v. National Cooperative Refinery Association,
Fifth, the type of relief plaintiffs request weighs strongly in favor of invoking primary jurisdiction. Primary jurisdiction will often be invoked when a plaintiff seeks injunctive relief, because there is the greatest likelihood that a court’s order will interfere with administrative agency’s proceedings.
Shinault v. American Airlines, Inc.,
Based on the Schwartzman factors, the Court finds that plaintiffs’ claims for in-junctive relief should be stayed under the doctrine of primary jurisdiction. 13 If the Court were to order abatement, the Court’s order would almost certainly conflict with the EPA’s efforts at Tar Creek. The EPA routinely handles these matters, and cleanup of environmental hazards falls soundly within the EPA’s expertise. Plaintiffs’ claims for injunctive relief shall be stayed until the EPA relinquishes responsibility for the Tar Creek Superfund site.
IV.
Defendants assert that they can not be held liable for any chat deposited on lands held by members of the Quapaw tribe, because they were statutorily required to do so. They claim that Okla. Stat. tit. 50, § 4 immunizes them from liability for leaving chat and tailings on the surface of restricted Quapaw lands, because the federal government expressly authorized defendants’ actions. Section 4 provides that “[njothing which is done or maintained under the express authority of a statute can be deemed a nuisance.” Id. Plaintiffs respond that section 4 applies to claims for injunctive relief only, but that plaintiffs may still maintain an action for damages. There are two leading cases from the Oklahoma Supreme Court interpreting this statute.
In
E.I. Du Pont De Nemours Powder Company v. Dodson,
It is true that, whilst the Legislature may legalize an act which might otherwise be a nuisance, it cannot authorize the taking or damaging of private property for public use without just compensation. But plaintiffs’ right to just compensation is not involved in this proceeding. The sole relief sought herein is for the abatement of an alleged nuisance and this prayer cannot be granted.... Hence it has been held that, although a nuisance may be legalized, and therefore protected from indictment and against interference with it as a public nuisance, the one maintaining it may nevertheless be liable in damages to an individual for any damages he may sustain therefrom.
Id. at 1087-88. The plaintiffs’ claim for abatement of a nuisance was dismissed, because plaintiffs did not include a claim for monetary damages.
In a more recent case, the Oklahoma Supreme Court held that а city could not be held liable for nuisance when it constructed a drainage ditch with specific statutory authorization.
City of Bartlesville v. Ambler,
Defendants argue that their statutory authorization defense is applicable to claims for nuisance, regardless of the remedy sought by plaintiffs. Thеy argue that plaintiffs should have brought a claim under Okla. Const. Art. 2, § 23. However,
Du Pont
does not support defendants’ contention, as the Oklahoma Supreme Court expressly rejected the English rule denying monetary damages when an alleged nuisance has been authorized by the legislature.
Du Pont,
In addition, the statutory authorization cited by defendants does not attempt to regulate the environmental problems alleged by plaintiffs and does not contain the requisite specificity to plaintiffs’ claims. Defendants cite several statutes related to the leasing of Quapaw land for mining purposes, including: (1) Act of June 7, 1897, 30 Stat. 72; (2) Act of March 3, 1909, 35 Stat. 751; (3) the Department of the Interior’s 1921 regulations concerning use of allotted lands; (4) Act of March 3, 1931, 41 Stat. 26; (5) the form lease required by the 1921 regulations to obtain subsurface rights to Quapaw land; (6) the 1929 regulations from the Department of the Interi- *807 or requiring mining companies to leave chat on the property of Quapaw Indians after ore was removed; (7) the 1934 regulations creating a new form lease and permitting mining companies to mill ore off-site. After reviewing all of the sources, the Court finds that none of the legislative or administrative acts authorized defendants to create an environmental hazard. In Du Pont, the legislature regulated the storage of explosive materials because, even though there were inherent dangers associated with explosives, the use of explosives was a necessary evil. The regulations cited by defendants are primarily concerned with protecting the economic interest of tribal members, but the Court can not find any legislative intent to regulate mining due to environmental concerns. The public policy behind the regulation of mining activity оn restricted Quapaw lands should not be construed as a legislative authorization of a nuisance, and Okla. Stat. tit. 50, § 4 is not applicable.
V.
Defendants argue that summary judgment is proper in their favor on plaintiffs’ claim for punitive damages, because there is no evidence that the mining defendants had knowledge of any dangers from lead contamination. Plaintiffs respond that the evidence produced during discovery shows that defendants’ actions at least constitute reckless disregard under Okla. Stat. tit. 23, § 9.1. Plaintiffs cite 16 “highlights” supporting their claim for punitive damages.
After reviewing the evidence cited by plaintiffs, the Court notes several concerns with the type of evidence on which plaintiffs intend to rely to support their claim for punitive damages. It is clear that plaintiffs are not distinguishing between the mining defendants, Blue Tee and Gold Fields, and the lead mining industry as a whole. For example, plaintiffs cite historical documents suggesting that mining companies have known since the 1870s that lead constitutes a poison that poses a seriоus health risk. See Dkt. 432, Ex. 53, at 1 (letter from president of National Lead Company expressing concerns that ingestion of lead was harmful). Plaintiffs also cite minutes from the annual meeting of the Lead Industries Association expressing general concern that the lead mining industry was viewed less favorably than other types of mining industries. Plaintiffs characterize the response of mining companies, but not specifically the mining defendants in this case, to claims by the medical community of the risks of lead poisoning as attacks designed to mislead the public about legitimate health risks caused by lead contamination. For purposes of summary judgment, the Court will consider what evidence plaintiffs have to raise a genuine issue of material fact that Blue Fields and Gold Tee recklessly disregarded a health risk to plaintiffs. 15
Defendants rely heavily on the Supreme Court’s decision in
State Farm Mutual Automobile Insurance Company v. Campbell,
the harm caused was physical as opposed to economic; the tortious conduct evinced an indifference to or a reckless disrеgard of the health or safety of others; the target of the conduct had financial vulnerability; the conduct involved repeated actions or was an isolated incident; and the harm was the result of intentional malice, trickery, or deceit, or mere accident.
Id.
at 419,
Much of the
Campbell
opinion concerns judicial review of punitive damages following a jury verdict but, in dicta, the Supreme Court discussed evidentiary concerns that come into play when punitive damages are at issue. In
Campbell,
the Supreme Court stated “out-of-state conduct may be probative when it demonstrates the deliberateness and culpability of the defendant’s action in the state where it is tortious, but that conduct must have a specific nexus to the specific harm suffered by plaintiff.”
Id.
at 422,
As discussed above, the Court has some concern that much of plaintiffs’ evidence involves dissimilar, out-of-state conduct that was not directed towards plaintiffs. 16 However, plaintiffs have submitted sufficient evidence to raise a genuine issue of material fact as to whether Gold Fields and Blue Tee acted with reckless disregard. The summary judgment record contains deposition testimony and exhibits supporting plaintiffs’ assertions that CHAMP researchers felt pressured to tailor their results in favor of defendants. Dr. Maleoe testified that representatives of Gold Fields and Blue Tee encouraged her to bury research that supported a conclusion that lead from chat piles was a leading cause of problems in Tar Creek. Plaintiffs’ suggestion that defendants attempted to delay the EPA’s research is subject to conflicting interpretations. While the Court is not prepared to conclude that defendants’ requests to delay the EPA’s invеstigation are probative of reckless disregard, plaintiffs have submitted evidence which could lead to the inference that defendants may have had an improper motive to disrupt the EPA’s ongoing investigation, or that defendants may have been aware of an increased risk to children if soil remediation near residences did not *809 occur quickly. This evidence is sufficient to raise a genuine issue of material fact as to reckless disregard for the safety of others, and defendants motion for summary judgment should be denied.
IT IS THEREFORE ORDERED that Defendants Blue Tee Corp. and Gold Fields Mining Corporation’s Motion for Partial Summary Judgment (Dkt.# 360) and Supplement to Blue Tee and Gold Field’s Motion for Partial Summary Judgment (Dkt.# 421) are granted in part and denied in part: plaintiffs’ claims for in-junctive relief are stayed under the doctrine of primary jurisdiction pending completion of the EPA’s remediation of the Tar Creek Superfund Site; the motions are denied in all other respects.
Notes
. Gold Fields admits that Tri-State owned "a small portion of the land surface in Sectiоn 16-T29NR23E.” Dkt. #360, at 4. Plaintiffs claim that Gold Fields currently owns 150 acres in the northern part of Picher, and that this land is a significant source of lead contamination in Picher. However, it does not appear that Blue Tee owns any property within Tar Creek.
. For purposes of defendants’ summary judgment motion, it is undisputed that defendants processed tailings from at least these locations. These locations are relevant to defendants' argument that it conducted mining activities within Quapaw territory that were subject to federal regulation. Plaintiffs mention several other areas where defendants actively mined for the purpose of showing that defendants engaged in more extensive mining than the motion for summary judgment indicates.
. Defendants claim that the Department of Interior, through the United States Geological Survey, conducted annual inspections of mining operations from 1923 to 1954. The purpose of these inspections was to "ascertain if the mines and mills were being efficiently operated to conserve the interests оf the Indian owners of ore.” Dkt. # 362, Ex. 27, at 19.
. In 1985, the threshold blood lead level for medical treatment was 25 ug/dL. This level was lowered to 10 ug/dL in 1991.
. Defendants suggest that the EPA volunteered to undertake the cleanup of Tar Creek without financial support from defendants. However, the EPA began a remedial investigation, feasibility study, and remedial design ("RI/FS/RD”) following defendants’ failure to make a "good-faith offer.” Dkt. #361, Ex. 11, at 1-2.
. EPA documents show that PRPs initially refused the EPA's invitation to participate in OU4. The EPA offered to enter a consent decree with Blue Tee and Gold Fields in 1996 and 2000, but defendants declined both offers. Blue Tee and Gold Fields agreed to an Administrative Order on Consent (“AOC”) with the EPA on December 5, 2004, but the AOC does not suggest why defendants agreed to the AOC after refusing to participate in OU4 for eight years.
. The EPA viewed CHAMP as a useful supplemental program to its soil remediation efforts, but it felt that the clean up should move forward. Defendants also requests the EPA to consider the results of the CHAMP study before going forward with remediation. The EPA notified defendants it would permit them to submit any findings tо the EPA, but found that the current risk of lead poisoning was "unacceptably high.” Dkt. #421, Ex. E, at 1-3.
. Gray has not been adopted by the Indiana Supreme Court, nor has its holding been referenced in a published opinion by the courts of any other state.
. Defendants do not actually argue preemption, but the Tenth Circuit has considered these same issues under the doctrine of preemption. To be consistent with Tenth Circuit
*802
precedent, the Court finds that defendants' arguments should be construed as a motion for summary judgment on the theory that CERCLA preempts the state law remedy of abatement.
New Mexico v. General Elec. Co.,
. Plaintiffs argued that abatement is necessary because The Doe Run Resources Corporation ("Doe Run”) refused to participate in OU4. Now that Doe Run has settled, plaintiffs' need for injunctive relief has been greatly reduced, because Gold Fields and Blue Tee are already participating in OU4.
. Dоe Run has notified the Court that it has agreed to a settlement with plaintiffs, which is set for hearing on final approval.
. Defendants argue that plaintiffs' claim for injunctive relief should be dismissed, but Tenth Circuit precedent suggests a strong preference for entering a stay instead of dismissing claims without prejudice.
See Southern Utah Wilderness Alliance,
. The Oklahoma Supreme Court remanded to the trial court, because the city had not condemned the property that would be infringed upon by the ditch, nor had the city compensated plaintiffs for taking property under a theory of eminent domain.
. The parties are advised not to construe the Court’s ruling on summary judgment as an in limine ruling on the admissibility of evidence. The magistrate judge has ruled on the parties’ motions in limine, and those rulings are not addressed in this opinion. The Court's discussion focuses on the relevance of certain evidence to its ruling on defendants’ motion for summary judgment, but should not be relied upon in any other context.
. Evidentiary issues related to plaintiffs’ claim for punitive damages will be dealt with if the jury finds in phase one of the trial that defendants acted with reckless disregard. The Court is not ruling at this time as to the admissibility of evidence under Campbell.
