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Maine’s Proposed Climate Superfund Legislation: Borrowing a Page From CERCLA to Address Climate Costs

Two bills proposing to create a state-level climate cost recovery program are currently being considered by the Environment and Natural Resources Committee of the Maine Legislature. The first, introduced in late April 2025, is the proposed Maine Climate Superfund Act (LD 1808). The second, LD 1870, entitled An Act to Establish a Climate Superfund Cost Recovery Program to Impose Penalties on Climate Polluters, was printed on May 5, 2025. Both bills aim to recover the costs associated with climate adaptation by holding major fossil fuel production companies financially responsible. Modeled closely on the strict liability framework found in the Federal Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA)—the Superfund lawthe bills do not require proof of negligence or misconduct. Instead, responsibility is assigned based purely on a company’s historical contribution to greenhouse gas emissions.

Supporters argue that this approach is both pragmatic and fair. As Maine faces growing expenses from rising sea levels, more intense storms, forest degradation, and public health impacts alleged to be linked to climate change, the bills aim to ensure that those alleged to have contributed significantly to greenhouse gas emissions help fund the necessary adaptation measures. Critics, however, have raised concerns about the constitutionality of applying strict financial liability retroactively, and especially to a problem as globally diffuse as climate change.


Who Would Be Responsible, For What, And For What Period?

Under both LD 1808 and LD 1870, a "responsible party" is defined as any entity—or successor to such an entity—that extracted fossil fuels or refined crude oil and whose products are determined to have contributed more than one billion metric tons of greenhouse gas emissions globally. However, the two bills differ slightly in the period of emissions they seek to cover. LD 1808 targets emissions occurring between January 1, 2000, and December 31, 2024, while LD 1870 expands that timeframe to include emissions dating back to January 1, 1995. In both cases, liability is limited to entities with a sufficient legal nexus to the State of Maine to meet constitutional requirements.

Prior to making cost recovery demands for compensatory payments, DEP would be tasked with calculating each entity’s emissions share using a yet-to-be determined methodology, in conjunction with using publicly available greenhouse gas emissions factors published by the U.S. Environmental Protection Agency (EPA). Affiliated companies within a "controlled group" would be treated as jointly and severally liable, mirroring CERCLA’s treatment of multiple responsible parties at Superfund sites. Importantly, only entities with a sufficient legal nexus to Maine would be subject to liability, a provision likely intended to protect against constitutional challenges.


What Is the Collection Process and What Would The Collected Payments Be Used For?

Under both bills, DEP is authorized to issue cost recovery demands to responsible parties. These entities may choose to pay their assessed share in a lump sum or in nine annual installments, with interest. Each bill provides entities the right to seek reconsideration of an assessment or to pursue judicial review in Superior Court.

All payments collected from responsible parties would be deposited into a dedicated fund to be used by the State for climate change adaptation projects across Maine, including reinforcing public infrastructure, upgrading stormwater management systems, expanding nature-based solutions like wetlands restoration, and enhancing energy grid resilience. While LD 1808 emphasizes disadvantaged communities through implementation strategy and rulemaking, LD 1870 mandates that at least 35% of the funds be used specifically for adaptation projects benefitting low-income or environmental justice communities.


What Are The Hurdles Facing Any Such Program?

Both LD 1808 and LD 1870 draw from CERCLA's strict, joint and several liability model. While CERCLA focuses on the cleanup of discrete contaminated sites, Maine's proposed legislation seeks to address alleged widespread damages resulting from cumulative greenhouse gas emissions over decades. This expansion of Superfund principles into a global environmental context presents new complexities, particularly in establishing proportional responsibility for diffuse climate impacts.

Legal challenges can be expected, particularly concerning both proposed laws’ retroactivity, potential violations of the Commerce Clause, and Federal preemption (i.e., that the law intrudes upon areas traditionally governed by Federal environmental policy). These preemption concerns are further amplified by President Trump’s April 8, 2025 Executive Order entitled “Protecting American Energy From State Overreach,” which directs Federal agencies to challenge state-level policies that “burden or penalize” domestic energy production. While the scope and enforceability of the Executive Order remain to be clarified, it signals the start of an aggressive Federal posture that is likely to further complicate state-led efforts like the legislation being proposed in Maine, particularly where such efforts aim to directly target past conduct of large-scale fossil fuel producers.

In fact, both of Maine's proposals follow similar efforts undertaken in New York and Vermont, each of which are now facing lawsuits challenging their constitutionality—including two lawsuits filed by the U.S. Department of Justice just this past week. Anticipating these issues, sponsors for both of the bills have included a requirement that responsible parties have a sufficient nexus to the state of Maine and that DEP rely upon a detailed emissions attribution process utilizing publicly-available data to calculate liability.


How Do Maine’s Proposals Compare To New York’s Existing Climate Change Superfund Act?

While both of Maine’s proposals share several core features with New York’s recently-enacted Climate Change Superfund Act—notably the reliance on strict liability, proportional emissions attribution, and a state-administered fund for climate adaptation—there are key differences in design and scope.

First, the covered periods differ: Maine’s LD 1870 and 1808 look at emissions from 1995 to 2025 and 2000 to 2024, respectively, while New York’s Act covers 2000 to 2018​. Maine’s more extended window may capture a broader range of more recent emissions data, while New York’s cutoff predates several recent spikes in emissions and extreme weather events that resulted in significant natural resource and property damage.

Second, while both states target fossil fuel extractors and refiners, New York’s legislation specifies a total cost recovery target: it seeks to recover $75 billion, assessed over a 25-year period at approximately $3 billion per year​. Both of Maine’s bills, in contrast, apparently leave the calculation of costs attributable to climate-related damage in Maine to be determined by the DEP based on the state’s actual climate-related expenditures, without setting a predetermined target.

Third, New York’s law is quite explicit about how the collected funds must be spent, with specific allocations for nature-based solutions, energy infrastructure, stormwater upgrades, and projects benefiting disadvantaged communities. Maine’s bills similarly emphasize environmental justice drivers but grant broad discretion to the DEP to develop (via rulemaking) and implement a “Resilience Implementation Strategy.”

Finally, Maine’s legislation takes a more cautious approach to legal risks. Both bills explicitly require that entities subject to cost recovery have a “sufficient connection” to Maine—language that, presumably, is designed to withstand Commerce Clause challenges. New York’s law includes similar protections, but Maine’s more deliberate emphasis on nexus and reliance on "best available science" methodologies reflects a heightened sensitivity to the constitutional critiques already being levied against New York’s statute.


What Is The Status Of The Maine Bills

LD 1808 was printed on April 29, 2025, and referred to the Environment and Natural Resources Committee. LD 1870 followed shortly after (printed on May 5, 2025) and was referred to the same committee. A joint public hearing on both bills was held on May 5, 2025.

During the hearing, Maine DEP Commissioner Loyzim testified neither for nor against either bill but cautioned the Committee that adopting some version of either bill at this time would create a significant administrative burden for the agency. Commissioner Loyzim emphasized DEP would require substantial legal and technical resources to implement and potentially defend the program.

At the public hearing there was also some discussion among committee members about the possibility of carrying over one or both bills into the next legislative session. A work session is expected to be scheduled in the coming weeks. As of this writing, a Fiscal Note has not yet been published for either LD 1808 or LD 1870—an omission that may further complicate the Committee’s ability to assess the scope and feasibility of implementation.

As with many large-scale environmental legislative proposals, the future of LD 1808 and LD 1870 remain uncertain amid the myriad of legal, fiscal, and political complexities involved.

Maine PUC Solicits Renewable Energy Projects on PFAS-Contaminated Farmlands

Will There be Any Takers Re Development of Renewable Energy Projects on Maine PFAS-Contaminated Farmlands?


The Maine Public Utilities Commission has wasted little time in soliciting bids for renewable energy projects to be located on PFAS-contaminated farmland. Following the PUC’s August 12, 2024, order, the Commission opened a docket initiating the request for proposals (“RFP”) for development on PFAS-contaminated land. This docket is the next step in the process through which the Commission will solicit and select renewable energy projects to be developed on land contaminated with “forever chemicals” that can no longer be used for agricultural purposes. See my prior post for background.

Traditionally, once such a docket is open, the Commission will issue a formal RFP detailing the parameters of the solicitation for power purchase agreements. The RFP must adhere to the requirements of applicable laws and rules—here, that includes the Commission’s newly adopted Chapter 397 rule implementing the contaminated-lands procurement program. Deadlines for response can vary and are typically specified in each RFP.

After proposals are received, the Commission will begin proceedings involving review of the proposals and conferences with the proposed developers. The Commission has determined this docket will be a “secured case”—meaning that full access to the proposals and participation will be limited to parties and intervenors approved by the Commission. Some information or documents may be released by the Commission on a discretionary basis; typically, the Commission publishes information on winning bidders and their proposals following their selection.

While the Maine PUC has put the pieces in place to move this program forward, it remains to be seen whether there is any significant appetite within the renewable energy development sector to bite into this unique development opportunity. 

Maine Seeks to Grow Solar Farming on PFAS-Contaminated Farms

The Maine Legislature recently directed the Maine PUC to adopt rules that would require the Commission to initiate purchases of renewable energy from projects that are located on land contaminated with PFAS – the so-called “forever chemicals.”  The legislation was enacted in recognition of the fact that at least 60 farms in Maine have been rendered useless for farming due to the spreading of PFAS-contaminated sewage sludge as fertilizer – a practice that State regulators had encouraged for over a quarter century.

In 2022, amidst increased state and national scrutiny on PFAs, the Maine Legislature passed a law banning the use of sewage sludge as a soil amendment and requiring Maine DEP to investigate and conduct testing on farms across the state. Since then, Maine DEP has undertaken testing at hundreds of sites where septage or sewage sludge has been land-applied.  

PUC Rules Chapter 397: Procurement of Renewable Resources with a Preference for Projects Located on Contaminated Land is effective as of August 10, 2024. This new rule implementing the Legislative directive, establishes requirements for the procurement of energy and renewable energy credits (“REC”) and specifies that land contaminated with PFAS should be given preferential treatment in determining which projects to approve. After providing an opportunity for public comment, the Commission issued an order on July 24, 2024, responding to the comments and publishing the final version of Chapter 397. Under the final rule, the Commission must issue its first procurement RFP no later than November 10, 2024.

In reviewing proposals under this program, the Commission will first determine whether a project is an Eligible Class IA (i.e., renewable) resource project. If the project is eligible, the Commission will give preference to those located on PFAS-contaminated land that has been determined by the Maine Dept of Agriculture, Conservation & Forestry to no longer be useable for its current or historical agricultural purposes.

Further, projects eligible for selection must have a net positive value for Maine ratepayers. In particular, for the Commission to approve a project, the cost of the contract must be outweighed by the economic benefit to Maine ratepayers. Benefits may include renewable energy credits (“RECs”) sold below their market value to help the state meet its renewable energy goals, or, reduced transmission-related costs.

The possibility of renewable energy projects utilizing contaminated land may offer an alternative financial pathway for farmers and landowners whose means of livelihood have been taken away. Given the likely additional cost of developing such contaminated land and the strict project approval requirements put in place by Chapter 397, it is unclear whether solar developers will choose to engage in the RFP process. Hence, whether the intent of the Maine Legislature in setting up the framework for this program will be achieved is far from certain.

Maine DEP Issues PFAS in Products Concept Draft Rule

The Maine DEP’s PFAS in Products Program has released its long-awaited Chapter 90 concept draft language (the “PFAS in Products Rule”) for implementation of Maine’s recently-amended “PFAS in Products Law.” The concept draft provides additional details on sales prohibitions for products and product components containing intentionally added PFAS, along with criteria DEP will require as part of forthcoming Currently Unavoidable Use (“CUU”) proposals for products or product categories with upcoming sale prohibitions in the State.

The release of the concept draft of the PFAS in Products Rule was made as part of an informal outreach process through which DEP is soliciting public input. Comments are due August 30, 2024; DEP plans to proceed with formal rulemaking later this fall.

“Currently unavoidable use” is defined in Maine’s PFAS in Products Law as a use of PFAS that DEP has determined by rule to be “essential for health, safety or the functioning of society and for which alternatives are not reasonably available.” See 38 M.R.S. § 1614.

Notably, under the concept draft the Department will only consider CUU proposals submitted between 18 and 36 months in advance of an applicable sales prohibition. Thus, absent an exemption to this timeframe, it does not appear DEP will entertain any CUU proposals for the following products or product categories containing intentionally added PFAS with sales prohibitions set to take effect on January 1, 2026:

  • cleaning products
  • cookware products
  •  cosmetic products
  • dental floss
  • juvenile products
  • menstruation products
  • textile articles
  • ski wax
  • upholstered furniture

Similarly, it appears DEP would not begin to consider CUU proposals for artificial turn and outdoor apparel for severe wet conditions not otherwise accompanied by a PFAS disclosure—the next two product categories with sales bans set to take effect January 1, 2029—until January 1, 2026 at the earliest.  

Individuals with comments on or concerns regarding the concept draft are encouraged to e-mail DEP’s PFAS in Products Program at PFASproducts@maine.gov

Preti Flaherty's Environmental Practice Group is closely monitoring Maine DEP's efforts regarding PFAS-related matters. Contact Kevin Osantowski or David Van Slyke if you have any questions on this topic.

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Preti Flaherty attorneys David Van Slyke and Kevin Osantowski contributed to this article.

Biden Administration’s Intent to Designate PFOA and PFOS as CERCLA Hazardous Substances

On January 10, 2022, the U.S. Environmental Protection Agency took a significant step towards fulfilling a Biden Administration goal of bringing per- and polyfluoralkyl substances (“PFAS”) under the regulatory purview of the Comprehensive Environmental Response, Compensation & Liability Act (“CERCLA”) by submitting to the White House Office of Management and Budget a formal plan to designate two PFAS compounds – perfluorooctanoic acid (“PFOA”) and perfluorooctanesulfonic acid (“PFOS”) – as hazardous substances.

The EPA’s submittal of the proposed rule to the OMB comes after years of delay and several resets to its prior efforts to designate PFAS compounds as hazardous substances under CERCLA and triggers a 90-day review period. Provided the OMB does not take issue with EPA’s proposed rule, at the conclusion of the 90-day review period EPA can publish it in the Federal Register for public comment. Barring setbacks, the EPA could issue a final rule in the summer of 2023. This timeline matches what the Agency laid out in its October 2021 PFAS roadmap.[1] Once implemented, the final rule is likely to trigger a cascade of regulatory requirements including but not limited to release reporting. As the EPA noted in its Fall 2021 Statement of Regulatory Priorities, a hazardous substance designation “would require facilities across the country to report on PFOA and PFOS releases that meet or exceed the reportable quantity assigned to these substances [so as to] enable federal, state, tribal, and local authorities to collect information regarding the location and extent of releases.”[2] The final rule would also permit the EPA and other agencies to seek cost recovery or contribution for costs incurred in connection with cleanup of PFOA and PFOS contamination, as well as subject sites that are or were previously listed on the National Priorities List as Superfund sites to additional review for concerns related to PFAS contamination.

The recent action is yet another indication of the strong desire by the Biden Administration to implement an aggressive federal regulatory framework to address PFAS contamination. Time will tell whether and to what extent federal and state regulatory agencies are willing to utilize any forthcoming hazardous substance designations as a basis for re-engaging potentially responsible parties to fund and/or perform additional remedial measures at Superfund sites to address existing PFAS contamination.

PretiFlaherty attorneys Kevin Osantowski and Jeff Talbert contributed to this article.
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[1] See Office of Land and Emergency Management, PFAS Strategic Roadmap: EPA’s Commitments to Action 2021-2024, U.S. EPA, https://www.epa.gov/pfas/pfas-strategic-roadmap-epas-commitments-action-2021-2024#olem (last visited Jan. 12, 2022).

[2] See Office of Information and Regulatory Affairs, Fall 2021 Unified Agenda of Regulatory Actions: EPA Statement of Priorities, Executive Office of the President, https://www.reginfo.gov/public/do/eAgendaMain (last visited Jan. 12, 2022).

Maine’s Proposed Climate Superfund Legislation: Borrowing a Page From CERCLA to Address Climate Costs

Two bills proposing to create a state-level climate cost recovery program are currently being considered by the Environment and Natural Reso...