This bill adds a new subsection to section 4005 of the Solid Waste Disposal Act that creates a formal designation—"beneficial use staging unit"—for coal combustion residuals (CCR) units that will be used as temporary storage before removal for beneficial use. It sets an application process, approval criteria tied to existing liner and groundwater-monitoring standards, a requirement that designated units stop receiving additional CCR, and an EPA/state enforcement path for designation and revocation.
The statute also changes regulatory treatment: a compliant staging unit is treated as a sanitary landfill under the Act, the EPA will publish annual, state-by-state reports, and the bill blocks state or local laws that conflict with the new framework. The change aims to accelerate reuse markets and extraction opportunities while carving out a federally uniform route that can limit state closure mandates and shift how owners/operators handle aging ash sites.
At a Glance
What It Does
Creates a new designation allowing certain lined, monitored CCR surface impoundments and landfills to be temporarily reclassified as staging units for removal and beneficial reuse, subject to a submitted management plan and state or EPA approval. It prohibits further receipt of CCR into a designated unit and permits revocation for noncompliance.
Who It Affects
Owners and operators of CCR surface impoundments and landfills, State agencies that run approved permit programs (or the EPA where states do not participate), downstream beneficial-use industries (construction materials, mineral recovery), and local governments that regulate site closures.
Why It Matters
The bill creates a federally defined pathway to keep existing CCR storage units open for product recovery rather than forcing immediate closure—reworking the practical balance between closure, reuse markets, and state-level closure requirements while adding a national reporting requirement.
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What This Bill Actually Does
The bill authorizes owners or operators of coal combustion residuals units to apply to their State (if the State runs an approved permit or prior-approval program) or to the EPA in nonparticipating States to have a unit designated as a beneficial use staging unit. Applications must include an attestation of compliance with the applicable beneficial-use obligations, a volumetric accounting of the CCR on site, and a plan describing how much material will be removed, when removal will occur, whether any critical minerals will be recovered, and the intended markets for the material.
Approval hinges on existing environmental protections: the unit must be a surface impoundment or landfill, be lined to the same standards already in federal or equivalent state rules, maintain the statutory groundwater-monitoring programs, and be in compliance with otherwise applicable federal or state regulations. States (or the EPA where applicable) can approve or deny applications and must inform applicants of denials; they can also revoke designations if the unit ceases to meet the liner, monitoring, or compliance conditions tied to the approval.Once designated, a unit may not accept additional CCR.
The statute treats a compliant beneficial use staging unit as a sanitary landfill under the Act and exempts it from a specific federal closure trigger that would otherwise force closure earlier than the staging unit’s removal schedule. The designation can be applied multiple times for a single unit unless the owner/operator previously failed to meet the applicable beneficial-use obligations.The EPA must publish an annual, state-by-state report that lists volumes stored and volumes removed for each designated unit and discloses the number of revocations.
States are required to provide necessary information to the EPA for that report. Finally, the bill contains an express federal-preemption clause: States and political subdivisions cannot enforce laws or orders that conflict with the new staging-unit rules, including directives that would close a compliant staging unit earlier than the federal schedule allows.
The Five Things You Need to Know
The bill requires owners/operators of designated staging units to remove at least 25% of the CCR stored in the unit.
Units holding fewer than 1.5 million cubic yards must meet the removal target by the earlier of: 5 years after removal begins or 7 years after designation.
Units holding 1.5 million cubic yards or more must meet the removal target by the earlier of: 10 years after removal begins or 12 years after designation.
Upon designation, the unit may not receive additional CCR and remains eligible for the staging classification only while it meets liner, groundwater-monitoring, and regulatory-compliance criteria.
The EPA must publish an annual report (first due March 1, 2026) with state-level breakdowns of CCR volumes stored, volumes removed for beneficial use, and the number of designation revocations; States must supply the data.
Section-by-Section Breakdown
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Application requirements for designation
This provision sets out what owners/operators must submit to seek the staging-unit label: an attestation of commitment to the beneficial-use requirement, a cubic-yard measurement of stored CCR, and a beneficial-use management plan. The plan must show removal volumes, a removal schedule, any plans to recover critical minerals (using the Energy Act of 2020 definition), and identified markets. Practically, this forces applicants to demonstrate a credible path to downstream use or recovery before they keep a unit open as a staging site.
Approval criteria and decision authority
States that operate approved permitting/prior-approval programs may decide applications; in nonparticipating States the EPA decides. The unit must be a surface impoundment or landfill, meet lining standards equivalent to 40 C.F.R. parts cited in the bill, and satisfy groundwater-monitoring requirements. This clause ties staging approvals tightly to existing technical safeguards, making regulatory compliance the threshold for receiving or keeping the staging designation.
Duration, repeat designations, and removal obligation
Designation is time-limited and ends when the statutory removal obligation is due; owners may seek multiple designations unless they previously failed to comply. The statute obligates owners to remove a portion of the material for beneficial use according to the submitted plan. Collectively, these provisions are designed to ensure staging is a transitional posture—intended to move material into beneficial markets rather than to indefinitely defer closure.
Prohibition on receiving CCR, sanitary-landfill status, and revocation
Once a unit is designated it cannot accept additional CCR. While compliant, the unit is treated as a sanitary landfill under the Act and is shielded from a specific federal closure trigger that would otherwise force earlier closure. The State or EPA can revoke a designation if the unit fails to maintain compliance with liner, monitoring, or applicable regulatory requirements—establishing a compliance-backed escape valve to pull staging status if environmental protections lapse.
Reporting, State cooperation, and preemption; definitions
The EPA must issue annual, State-by-State reports on stored and removed CCR volumes and revocations; States must feed EPA the necessary data. The provision includes an express federal-preemption clause preventing States or localities from imposing conflicting rules, including orders that would close a compliant staging unit earlier than the federal schedule. The subsection concludes with definitions (e.g., designation date, nonparticipating State) that pin down operational terms used elsewhere in the text.
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Explore Environment in Codify Search →Who Benefits and Who Bears the Cost
Every bill creates winners and losers. Here's who stands to gain and who bears the cost.
Who Benefits
- Owners and operators of CCR surface impoundments and landfills — they get a federally sanctioned route to keep units open to remove material for reuse rather than closing immediately, which can defer closure costs and create time to monetize ash.
- Construction and materials manufacturers (e.g., cement, concrete, road-base producers) — increased, predictable access to CCR feedstock can lower input costs and expand supply for beneficial-use markets.
- Critical-mineral recovery companies — the bill explicitly allows recovery plans for critical minerals from CCR, opening a regulated supply source for downstream processing and investment.
- EPA and States with approved programs — the framework centralizes reporting and creates clearer criteria for approvals and enforcement, aiding program planning and national data collection.
Who Bears the Cost
- State environmental agencies — they will need to review applications, provide data for EPA reports, and conduct oversight or revocation actions, potentially without new appropriations.
- Utilities and site owners that lack ready beneficial-use markets — they must prepare management plans, fund removal or contracts for removal, and maintain liner/monitoring standards while marketing material.
- Local governments and communities near CCR sites — they may bear increased long-term monitoring and environmental-justice risk if staging extends the period CCR remains onsite instead of triggering immediate closure and remediation.
- Closure and remediation contractors — market demand for closure work may decline or shift, creating economic dislocation and the need to adapt services toward material recovery rather than cap-and-contain closures.
Key Issues
The Core Tension
The core dilemma: accelerate CCR reuse to recover value and critical minerals versus maintain strict closure and remediation to protect health and the environment—this bill prioritizes a regulated, federally uniform route for reuse that can delay closure, but doing so risks extending onsite exposure and ceding state/local tools for forcing remediation when markets or enforcement are weak.
The bill creates a federal pathway that incentivizes keeping CCR onsite temporarily while pursuing beneficial use. That design addresses a real economic barrier to reuse—lack of time to build markets—but it raises implementation questions.
The statute ties approval to existing liners and groundwater monitoring, but it does not add new financial-assurance or long-term liability provisions specific to staging units; regulators will need to decide whether current bonding and post-closure care frameworks are adequate when units remain active longer for removal campaigns. Enforcement hinges on States and the EPA having the capacity to verify volumetric claims, removal timelines, and market commitments—tasks that will require clear guidance on measurements, audit rights, and penalties for falsified plans.
Preemption is another operational tension. By forbidding state or local measures that conflict with the staging framework—explicitly including closure mandates—the bill creates a uniform national rule, but it also removes avenues states and communities currently use to force site closures.
That may speed beneficial-use projects in some places while limiting protective action where local authorities judge a site hazardous. Finally, the policy assumes adequate beneficial-use markets will materialize; if markets lag, owners could meet the statutory minimums via low-quality uses or by contracting for removal without meaningful long-term risk reduction, undermining environmental goals the Solid Waste Disposal Act originally targeted.
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