Florida Power Corp. v. FirstEnergy Corporation

810 F.3d 996, 2015 FED App. 0269P, 81 ERC (BNA) 1609, 2015 U.S. App. LEXIS 19309, 2015 WL 6743513
CourtCourt of Appeals for the Sixth Circuit
DecidedNovember 5, 2015
Docket14-4126
StatusPublished
Cited by26 cases

This text of 810 F.3d 996 (Florida Power Corp. v. FirstEnergy Corporation) is published on Counsel Stack Legal Research, covering Court of Appeals for the Sixth Circuit primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Florida Power Corp. v. FirstEnergy Corporation, 810 F.3d 996, 2015 FED App. 0269P, 81 ERC (BNA) 1609, 2015 U.S. App. LEXIS 19309, 2015 WL 6743513 (6th Cir. 2015).

Opinions

GRIFFIN, J., delivered the opinion of the court in which STAFFORD, D.J., joined. SUHRHEINRICH, J. (pp. 1010-19), delivered a separate dissenting opinion.

OPINION

GRIFFIN, Circuit Judge.

Almost seventy years ago, plaintiffs predecessor in interest owned and operated two coal gasification plants in Florida. In 1998 and 2003, plaintiff entered into Administrative Orders by Consent (“AOCs”) with the U.S. Environmental Protection Agency to assess the feasibility of remediation of environmental contamination at those sites. At issue in this case is the narrow legal question of whether those AOCs constitute “administrative settlements” for purposes of the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (“CERCLA”), 42 U.S.C § 9601 et seq. We hold that they do not. We therefore reverse the district court’s dismissal of plaintiffs contribution action based on the statute of limitations and remand for further proceedings.

I.

This case involves two Florida plants, one in Sanford and the other in Orlando. After discovering hazardous contaminants [999]*999on those sites in the 1990s, the EPA concluded that plaintiff Florida Power Corporation, along with other previous owners of those sites, was liable for costs associated with removal and remediation of contamination. In 1998, plaintiff entered into an “Administrative Order by Consent for Remedial Investigation/Feasibility Study” with the EPA for the Sanford site (“Sanford AOC”). In 2003, it entered into a similar agreement of the same title for the Orlando site (“Orlando AOC”).

Under the terms of the AOCs, plaintiff agreed to conduct and implement a remedial investigation and feasibility study for each site. The remedial investigation was intended to determine the nature and extent of the public safety threat. The feasibility study was designed to identify and evaluate options for remedial action. The AOCs established a plan for implementation and set monetary penalties for violating the plan. Plaintiff also agreed to pay the EPA $429,731.23 for past response costs it had incurred at the Sanford site and $104,751.46 for such costs at the Orlando site. Following completion of the investigation and study at the Sanford site, the EPA entered three Records of Decision — in 2000, 2001, and 2006. On January 16, 2009, the U.S. District Court for the Middle District of Florida approved a consent decree between plaintiff and the EPA for actual performance of remediation at the Sanford site. Regarding the Orlando site, plaintiff submitted a draft Remedial Investigation Report, Risk Assessment, and Remedial Alternative Technical Memorandum that was under review by the EPA at the time of this litigation.

On December 30, 2011, plaintiff filed this cost recovery and contribution CERCLA action in the Middle District of Florida for costs related to both sites. It also sought a declaratory judgment that defendant, as a successor in interest to a former owner-operator of the sites, was liable for future response costs that plaintiff would incur. Upon defendant’s motion, the case was transferred to the Northern District of Ohio. Defendant moved for judgment on the pleadings under Federal Rule of Civil Procedure 12(c) on the basis that the 1998 and 2003 AOCs had triggered CERCLA’s three-year statute of limitations and plaintiffs claims were therefore barred. Initially, the district court denied the motion on the grounds that the Sanford AOC was not a settlement agreement because it did not release any party from any liability and preserved the EPA’s right to sue plaintiff for CERCLA violations. Regarding the Orlando AOC, the court ruled that plaintiff could only bring a cost recovery action because the AOC “by its own terms, was not a settlement agreement.”

However, on reconsideration, following our decision in Hobart Corp. v. Waste Management of Ohio, Inc., 758 F.3d 757 (6th Cir.2014), the district court reversed itself and dismissed plaintiffs claims because it concluded the AOCs at issue resembled the settlement agreement in Hobart and therefore triggered the statute of limitations. We disagree and, for the reasons stated herein, reverse and remand for further proceedings.

II.

A.

“The district court’s decision regarding a motion for judgment on the pleadings pursuant to Federal Rule of Civil Procedure 12(c) is analyzed using the same de novo standard of review employed for a motion to dismiss under Rule 12(b)(6).” Tucker v. Middleburg-Legacy Place, 539 F.3d 545, 549 (6th Cir.2008). We take as true all well-pleaded material allegations in the opposing party’s pleadings, and affirm the district court’s grant [1000]*1000of the motion only if the moving party is entitled to judgment as a matter of law. JPMorgan Chase Bank, N.A. v. Winget, 510 F.3d 577, 581 (6th Cir.2007).

Broadly speaking, CERCLA “facilitates cleanup and remediation of contaminated lands, and shifts the financial burden of such environmental response actions to the parties responsible for releasing hazardous substances.” ITT Indus., Inc. v. BorgWarner, Inc., 506 F.3d 452, 456 (6th Cir.2007); see Walls v. Waste Res. Corp., 823 F.2d 977, 981 (6th Cir.1987). The statute imposes liability on several categories of potentially responsible parties (“PRPs”), including current owners or operators of a contaminated facility, owners or operators of a facility at the time hazardous substances were disposed, any person who arranged for disposal of such hazardous substances at a facility, and any person who accepted such hazardous substances for transport to disposal or treatment facilities. 42 U.S.C. § 9607(a)(l)-(4). When the EPA identifies a contaminated site, it has several options. It may clean up the site itself under CERCLA § 104, 42 U.S.C. § 9604, compel a PRP to clean up the site under § 106, id. § 9606, or enter into an agreement under § 122 by which a PRP agrees to clean up the site, id. § 9622. Hobart, 758 F.3d at 762.

CERCLA provides two express cost-shifting actions for costs incurred in remediating a site. Under the “cost recovery” provision of CERCLA § 107(a)(4), the EPA may bring an action against PRPs to recover “all costs of removal or remedial action incurred by the United States Government.” 42 U.S.C. § 9607(a)(4)(A). A PRP that cleans up a site may likewise bring a cost recovery action against other PRPs. See id. § 9607(a)(4)(B); ITT Indus., 506 F.3d at 456.

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810 F.3d 996, 2015 FED App. 0269P, 81 ERC (BNA) 1609, 2015 U.S. App. LEXIS 19309, 2015 WL 6743513, Counsel Stack Legal Research, https://law.counselstack.com/opinion/florida-power-corp-v-firstenergy-corporation-ca6-2015.