9.2 CERCLA Superfund Process & RCRA Corrective Action

Key Takeaways

  • CERCLA (Superfund, 42 U.S.C. § 9601 et seq.) establishes strict and retroactive liability, with joint-and-several liability when the harm is indivisible across four classes of Potentially Responsible Parties (PRPs): Current Owners/Operators, Past Owners/Operators during disposal, Arrangers/Generators, and Transporters who selected the disposal site.
  • The National Contingency Plan (NCP, 40 CFR Part 300) governs the 8-stage Superfund remedial pipeline: PA/SI → Hazard Ranking System (HRS score ≥ 28.5 makes a site eligible for proposed NPL listing; listing is not automatic) → RI/FS → Proposed Plan & 30-day public comment → Record of Decision (ROD) → RD/RA → Construction Completion & O&M → NPL Deletion with mandatory 5-Year Reviews.
  • Remedy selection under CERCLA RI/FS must evaluate alternatives against 9 Criteria grouped into Threshold Criteria (Protection of Human Health/Env, ARARs compliance), Primary Balancing Criteria (Long-term effectiveness, Toxicity/mobility/volume reduction via treatment, Short-term effectiveness, Implementability, Cost), and Modifying Criteria (State and Community acceptance).
  • Applicable or Relevant and Appropriate Requirements (ARARs) encompass chemical-specific (MCLs), location-specific (wetlands, floodplains), and action-specific (RCRA capping, air discharge limits) cleanup standards.
  • RCRA Corrective Action (RCRA §§ 3004(u)/(v) and 3008(h)) parallels the CERCLA pipeline to address releases at Solid Waste Management Units (SWMUs) across four sequential phases: RCRA Facility Assessment (RFA) → RCRA Facility Investigation (RFI) → Corrective Measures Study (CMS) → Corrective Measures Implementation (CMI).
Last updated: August 2026

CERCLA Superfund Process & RCRA Corrective Action

When uncontrolled hazardous substance releases threaten human health or environmental ecosystems, federal statutory frameworks mandate rigorous, legally enforceable remediation pathways. The two paramount statutory mechanisms in the United States are:

  1. The Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA), commonly known as Superfund (42 U.S.C. § 9601 et seq.), enacted in 1980 and amended by the Superfund Amendments and Reauthorization Act (SARA) of 1986.
  2. The Resource Conservation and Recovery Act (RCRA) Corrective Action Program codified under RCRA §§ 3004(u)/(v) and 3008(h) and RCRA § 3004(u)/(v) & § 3008(h), addressing releases at active, permitted, or legacy hazardous waste Treatment, Storage, and Disposal Facilities (TSDFs).

Certified Hazardous Materials Managers (CHMMs) must navigate the liability provisions, evaluation criteria, remedial pipelines, and statutory cleanup standards governing both programs.


1. CERCLA Statutory Liability & Potentially Responsible Parties (PRPs)

CERCLA is renowned for having the most sweeping and formidable liability structure in American jurisprudence. Under CERCLA § 107(a), liability is:

  • Strict: Fault, negligence, or state-of-mind is irrelevant; liability is established solely by demonstrating that a release or threatened release of a hazardous substance occurred from a facility causing response costs.
  • Joint and Several: Any single liable party can be held responsible for 100% of the total site cleanup costs, regardless of their relative volumetric contribution, unless that party can prove divisibility of harm (which is extraordinarily rare).
  • Retroactive: Liability applies to acts and disposals that occurred decades prior to the enactment of CERCLA in 1980.
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|              THE FOUR CLASSES OF POTENTIALLY RESPONSIBLE PARTIES (PRPs)     |
|                                                                             |
|   [1] CURRENT OWNER OR OPERATOR                                             |
|   - Current fee-title owner or active facility operator of the facility.   |
|                                                                             |
|   [2] PAST OWNER OR OPERATOR AT TIME OF DISPOSAL                            |
|   - Any entity that owned or operated the site when hazardous substances    |
|     were disposed of, spilled, or placed on site.                           |
|                                                                             |
|   [3] GENERATOR / ARRANGER                                                  |
|   - Any person who arranged for disposal, treatment, or transport of        |
|     hazardous substances owned or possessed by them to the facility.        |
|                                                                             |
|   [4] TRANSPORTER                                                           |
|   - Any person who accepted hazardous substances for transport to a site    |
|     selected by the transporter.                                            |
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2. The Superfund Remedial Pipeline (NCP - 40 CFR Part 300)

The National Oil and Hazardous Substances Pollution Contingency Plan (NCP), codified at 40 CFR Part 300, establishes the formal administrative and engineering blueprint for Superfund cleanup operations:

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|                         THE 8-STAGE CERCLA SUPERFUND REMEDIAL PIPELINE                  |
|                                                                                         |
|   1. PA / SI   --> 2. HRS SCORING --> 3. RI / FS   --> 4. PROPOSED PLAN & PUBLIC COMMENT|
|   (Initial Site    (Score ≥ 28.5      (Delineate Plume    (30-Day Public Review         |
|    Inspection)      Qualifies NPL)     & Screen 9 Criter)  of Preferred Alternative)    |
|        |                                                                                |
|        v                                                                                |
|   5. ROD       --> 6. RD / RA     --> 7. O&M / CC  --> 8. NPL DELETION; 5-YR REVIEWS IF REQUIRED   |
|   (Record of       (Engineering       (Operate, Treat,    (Cleanup Complete; Five-Year  |
|    Decision)        Design & Build)    Inspect Systems)    Reviews if Waste Remains)    |
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Detailed Breakdown of NCP Pipeline Stages:

1. Preliminary Assessment / Site Inspection (PA/SI)

  • PA: Low-cost desk review of historical records, site data, and migration pathways to determine if the site poses potential threats.
  • SI: Targeted field sampling of media (groundwater, soil, surface water) to confirm release presence and target populations.

2. Hazard Ranking System (HRS) & National Priorities List (NPL)

  • The Hazard Ranking System (HRS) is a mathematically structured, numerically scored assessment model evaluating the relative potential risk posed by a site across four migration pathways:
    1. Groundwater Migration Pathway (drinking water aquifer threats).
    2. Surface Water Migration Pathway (drinking water intakes, human food chain, sensitive aquatic environments).
    3. Soil Exposure and Subsurface Intrusion Pathway (direct contact, resident populations, vapor intrusion).
    4. Air Migration Pathway (atmospheric dispersion to population centers).
  • The NPL Cutoff Score: An overall HRS score of HRS28.5\text{HRS} \ge 28.5 (on a 0–100 scale) qualifies the site for listing on the National Priorities List (NPL), making it eligible for long-term federal Superfund Trust Fund financing.

3. Remedial Investigation / Feasibility Study (RI/FS)

  • Remedial Investigation (RI): Comprehensive field data collection to determine the nature, three-dimensional spatial extent, volume, and fate/transport of contamination, culminating in a Baseline Risk Assessment (BRA) quantifying cancer and non-cancer risks.
  • Feasibility Study (FS): Development, screening, and detailed comparative evaluation of engineering cleanup alternatives against the Nine CERCLA Evaluation Criteria.

4. Proposed Plan & Public Comment Period

EPA drafts a Proposed Plan identifying the preferred remedial alternative and rationale. The agency provides at least a 30-day public comment period and an opportunity for a public meeting; the comment period may be extended.

5. Record of Decision (ROD)

The Record of Decision (ROD) is the formal legal document issued by EPA that details the selected site remedy, addresses public comments via a Responsiveness Summary, and establishes legal performance and cleanup standards.

6. Remedial Design / Remedial Action (RD/RA)

  • Remedial Design (RD): Preparation of detailed engineering specifications, blueprints, construction plans, and equipment procurement documents.
  • Remedial Action (RA): Actual construction, system installation, earthmoving, treatment plant erection, and startup.

7. Construction Completion & Operation and Maintenance (O&M)

  • Construction Completion: Physical construction of all remedial infrastructure is complete (even if pump-and-treat or bioremediation systems must operate for decades).
  • O&M: Ongoing operation, routine sampling, monitoring well gauging, cap maintenance, and mechanical servicing.

8. NPL Deletion & Mandatory Five-Year Reviews

  • NPL Deletion: Once all cleanup goals established in the ROD are achieved and verified, EPA initiates formal rulemaking to delete the site from the NPL.
  • Five-Year Reviews (CERCLA § 121(c)): If the selected remedy results in hazardous substances, pollutants, or contaminants remaining on site above levels that allow for unlimited use and unrestricted exposure, EPA is legally mandated to conduct a comprehensive formal review at least every five (5) years to verify that the remedy remains protective of human health and the environment.

3. The Nine CERCLA Evaluation Criteria & ARARs

Under 40 CFR § 300.430(e)(9)(iii), all remedial alternatives in the Feasibility Study must be evaluated against Nine Evaluation Criteria, structured into three statutory tiers:

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|                             THE NINE CERCLA EVALUATION CRITERIA                         |
|                                                                                         |
|   [TIER 1: THRESHOLD CRITERIA] (Mandatory Pass/Fail Gates - Must be satisfied)          |
|   1. Overall Protection of Human Health and the Environment.                            |
|   2. Compliance with Applicable or Relevant and Appropriate Requirements (ARARs).       |
|                                                                                         |
|   [TIER 2: PRIMARY BALANCING CRITERIA] (Trade-off & Comparative Selection Factors)      |
|   3. Long-Term Effectiveness and Permanence.                                            |
|   4. Reduction of Toxicity, Mobility, or Volume Through Treatment.                      |
|   5. Short-Term Effectiveness (Worker safety, community impacts during construction).   |
|   6. Implementability (Technical feasibility, administrative permitting, equipment).    |
|   7. Cost (Capital cost, annual O&M, Net Present Value / NPV).                          |
|                                                                                         |
|   [TIER 3: MODIFYING CRITERIA] (Evaluated after public comment period)                  |
|   8. State / Support Agency Acceptance.                                                 |
|   9. Community Acceptance.                                                              |
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Applicable or Relevant and Appropriate Requirements (ARARs)

Under CERCLA § 121(d), on-site Superfund response actions are exempt from obtaining formal administrative permits (e.g., NPDES or RCRA permits), but they must strictly comply with substantive federal and state environmental standards, designated as ARARs:

ARAR CategoryDefinition & Legal PurposeConcrete Practical Examples
Chemical-Specific ARARsHealth- or risk-based concentration limits or numerical discharge standards in environmental media.Safe Drinking Water Act Maximum Contaminant Levels (MCLs) for groundwater (e.g., $5,\mu\text{g/L}$ for Benzene or TCE); Clean Air Act National Ambient Air Quality Standards (NAAQS).
Location-Specific ARARsRestrictions placed on the concentration of hazardous substances or remedial activities due to specific geographic or ecological locations.Clean Water Act Section 404 / Executive Order 11990 (Protection of Wetlands); National Historic Preservation Act; Coastal Zone Management Act; Endangered Species Act restrictions.
Action-Specific ARARsTechnology- or activity-based requirements triggered by the specific execution of a remedial action.RCRA Subtitle C cap design requirements (40 CFR § 264.310); Clean Air Act VOC emission limits on air stripper off-gas; OSHA HAZWOPER (29 CFR § 1910.120) worker safety rules.

4. RCRA Corrective Action Process (RCRA §§ 3004(u)/(v) and 3008(h))

While CERCLA focuses primarily on abandoned, unpermitted, or legacy release sites, the RCRA Corrective Action Program mandates cleanups at operating, permitted, or interim status facilities that treat, store, or dispose of hazardous waste. Under RCRA § 3004(u) and (v), any facility seeking a RCRA hazardous waste permit must address releases of hazardous waste or constituents from any Solid Waste Management Unit (SWMU) regardless of when the waste was placed in the unit.

The RCRA SWMU Corrective Action Sequence:

+-----------------------------------------------------------------------------------------+
|                        RCRA CORRECTIVE ACTION MILESTONES (SUBPART S)                    |
|                                                                                         |
|   [1] RCRA FACILITY ASSESSMENT (RFA)                                                    |
|   - Conducted by regulatory agency (EPA or authorized State).                           |
|   - Identifies all SWMUs, Areas of Concern (AOCs), and potential release points.        |
|                                     |                                                   |
|                                     v                                                   |
|   [2] RCRA FACILITY INVESTIGATION (RFI)                                                 |
|   - Conducted by facility owner/operator.                                               |
|   - Fully delineates the nature, three-dimensional extent, and rate of release.         |
|                                     |                                                   |
|                                     v                                                   |
|   [3] CORRECTIVE MEASURES STUDY (CMS)                                                   |
|   - Facility identifies, screens, and evaluates potential engineering remedies.         |
|   - Recommends preferred remedy based on technical, human health, and cost factors.     |
|                                     |                                                   |
|                                     v                                                   |
|   [4] CORRECTIVE MEASURES IMPLEMENTATION (CMI)                                          |
|   - Agency approves Statement of Basis and issues final remedy selection.               |
|   - Facility designs, constructs, operates, maintains, and monitors the remedy.         |
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Direct Comparison: CERCLA vs. RCRA Corrective Action Pipelines

Process StepCERCLA Superfund Pipeline (40 CFR Part 300)RCRA Corrective Action Pipeline (statute, permit, or order)
Initial Site AssessmentPreliminary Assessment / Site Inspection (PA/SI)RCRA Facility Assessment (RFA)
Prioritization MetricHazard Ranking System (HRS $\ge 28.5 \rightarrow$ NPL)National Corrective Action Priority System (NCAPS)
Field CharacterizationRemedial Investigation (RI)RCRA Facility Investigation (RFI)
Remedy EvaluationFeasibility Study (FS - 9 Criteria)Corrective Measures Study (CMS)
Public Decision DocumentProposed Plan $\rightarrow$ Record of Decision (ROD)Statement of Basis $\rightarrow$ Final Remedy / Permit Mod
Engineering & ActionRemedial Design / Remedial Action (RD/RA)Corrective Measures Implementation (CMI)
Long-Term GovernanceFive-Year Reviews & NPL DeletionCorrective Action Complete Determination / Permit Release
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Comparative Alignment: CERCLA Superfund vs. RCRA Corrective Action
Test Your Knowledge

A historic chemical manufacturing site is evaluated by the EPA using the Hazard Ranking System (HRS). Following a Preliminary Assessment and Site Inspection (PA/SI), the site receives an overall HRS score of 32.4 based on documented chlorinated solvent contamination in a regional drinking water aquifer and adjacent wetland. What is the immediate regulatory consequence of this HRS score?

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B
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D
Test Your Knowledge

During the Feasibility Study (FS) for a Superfund site, an engineering firm evaluates five cleanup alternatives. Alternative A offers the lowest capital cost and rapid implementation, but fails to meet the Safe Drinking Water Act Maximum Contaminant Level (MCL) for vinyl chloride in the drinking water aquifer. Alternative B complies with all MCLs and protects human health, but has a higher capital cost and longer remediation timeframe. According to the Nine CERCLA Evaluation Criteria, how must the EPA treat Alternative A?

A
B
C
D
Test Your Knowledge

An active industrial facility holding a RCRA Part B hazardous waste storage permit discovers that an unlined historical solid waste management unit (SWMU) placed in operation in 1965 leaked trichloroethylene into underlying soils. Under RCRA Corrective Action provisions (RCRA §§ 3004(u)/(v) and 3008(h)), which specific sequential process must the facility follow to address the release?

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B
C
D
Test Your Knowledge

A Superfund remedial action was completed in 2021 at an NPL site where a hazardous waste landfill cap and an engineered slurry wall were installed. Hazardous contaminants remain contained in place beneath the cap above levels allowing unrestricted residential use. Under CERCLA § 121(c) and the National Contingency Plan, what recurring legal obligation is imposed on the EPA and responsible parties?

A
B
C
D