Jenkins Academy of Applied Technology

HZW-001-EPA — Learner reference

HAZWOPER Site Cleanup — OSHA and EPA Requirements · v1.0.0 · October 22, 2026

Course developed by Todd Jerome Jenkins, MS, CSP.

Understand EPA worker-protection coverage and cleanup-compliance duties: CERCLA/RCRA, ARARs, waste determination, accumulation, training, shipment, treatment, releases and closeout. Twelve audible knowledge lessons; allow about 40–55 minutes.

Requirements awareness only; no EPA certification, full RCRA facility training, DOT shipping qualification or HAZWOPER hours/field experience are awarded. Actual permits, agency decisions, role-specific instruction and site implementation remain separate. Requirements depend on the cleanup and jurisdiction.

1. Understand EPA worker-protection coverage

By the end: Identify the employer and jurisdiction for worker protection separately from environmental duties.

EPA’s worker-protection rule in 40 CFR Part 311 applies the substantive HAZWOPER provisions to state and local government employees engaged in covered operations in states without an OSHA-approved State Plan. It closes a public-employee coverage gap; it is not a reduced environmental-only version of worker protection.

For this rule, an employee includes compensated or uncompensated workers directly controlled by state or local government, as distinguished from independent contractors. Government-directed volunteers can therefore be covered. Private contractors have their own applicable occupational-safety obligations.

Where an approved State Plan applies, confirm that program’s public-employee coverage and requirements. Identify the employer, control relationship, jurisdiction and actual operation before choosing the compliance route. The same project can involve several employers and agencies.

Part 311 does not replace CERCLA, RCRA, water, air or other environmental requirements. This companion explains how to identify those duties, but provides neither regulatory training hours nor EPA certification of an employee or cleanup.

Basis: 40 CFR 311.1–311.2; 29 CFR 1910.120

2. Identify the cleanup authority and controlling documents

By the end: Locate the controlling cleanup documents and the person authorized to approve changes.

CERCLA, often called Superfund, addresses releases or threatened releases through removal and remedial actions. RCRA corrective action addresses releases at covered hazardous-waste facilities. State cleanup programs, orders, permits and agreements may also govern the project.

The applicable authority and controlling documents define objectives, approved work, sampling, reporting and completion conditions. A contractor’s work order does not authorize a different remedy or disposal method. Locate the current decision, order, permit or approved plan and its responsible agency contact.

Environmental compliance and worker safety plans answer different questions. A remedy can protect the community while still requiring detailed worker controls during excavation, treatment or sampling. Keep the workplan and site safety plan consistent as activities change.

Record who can approve changes and what must be submitted before action. Stop and escalate unexpected conditions that could change the remedy, waste classification, discharge route or protection measures. Do not interpret a contract deadline as regulatory authorization.

Basis: 40 CFR Part 300; RCRA corrective-action authorities; EPA cleanup guidance

3. Understand ARARs and the on-site permit boundary

By the end: Distinguish permit paperwork relief from the substantive requirements of the actual response.

Applicable or relevant and appropriate requirements, or ARARs, identify substantive environmental standards for CERCLA work. They may concern a chemical, location or action. The lead and support agencies determine site-specific requirements; guidance to be considered is distinguished from a binding regulation.

CERCLA remedial actions generally must attain ARARs unless a valid statutory waiver applies. Removal actions attain them to the extent practicable considering the situation’s exigencies. Workers and contractors do not grant themselves waivers.

The federal rule exempts qualifying on-site CERCLA response actions from obtaining federal, state or local permits. On-site has a defined contamination-area and close-proximity meaning. This is not a blanket exemption for every cleanup or everything inside an owner’s property boundary, and substantive requirements remain relevant.

Off-site response activities must obtain permits when required. Confirm the actual boundary, action authority, standards and agency-approved approach before treatment, discharge or transfer. A permit exemption does not authorize uncontrolled emissions or disposal.

Basis: 40 CFR 300.400(e),(g); 300.415(j); 300.430(f)

4. Make an accurate hazardous-waste determination

By the end: Have qualified personnel determine waste status before mixing, movement or disposal decisions.

RCRA requires an accurate hazardous-waste determination at the point of generation before dilution, mixing or other alteration. Reevaluate when management or environmental exposure may change the classification. Assign qualified responsibility and retain the supporting evidence.

Determine whether material is a solid waste, whether an exclusion applies, whether it meets a listed-waste description and whether it exhibits a hazardous characteristic. The characteristics are ignitability, corrosivity, reactivity and toxicity. Solid waste can include liquids and sludges; the everyday meaning of solid is misleading here.

Use reliable process knowledge and appropriate representative testing. If available knowledge is inadequate to determine a characteristic accurately, the specified testing is required. A negative characteristic test does not automatically cancel a listed-waste classification.

Soil, groundwater, debris, spent PPE and treatment residues may need different evaluations. Environmental cleanup targets and worker air limits do not establish RCRA status. Small and large quantity generators retain determination records at least three years from the waste’s last shipment to on-site or off-site treatment, storage or disposal, subject to extensions.

Basis: 40 CFR 262.11; 40 CFR Part 261

5. Determine generator category and accumulation duties

By the end: Verify the actual generator category and documented accumulation conditions.

Generator category depends on hazardous-waste amounts generated in a calendar month and the applicable acute-waste rules, not the business’s employee count. A cleanup can change the category. Identify who is the generator and which site identification and notification requirements apply.

Federal large quantity generators generally have a ninety-day accumulation limit; small quantity generators generally have 180 days, with a conditional 270-day provision when shipment requires 200 miles or more. These are conditional exemptions, not unconditional storage rights. Quantity limits, unit standards and other conditions still matter.

Very small quantity generators have different limits and destination conditions. Satellite accumulation has its own location, control, quantity and container requirements; do not label every storage area satellite to avoid central-area duties. Authorized states can impose stricter or additional requirements.

The environmental lead must document the current category, counting method, accumulation areas, dates and applicable conditions before waste builds up. Do not assume an episodic-generation provision applies automatically to a one-time cleanup; verify every condition and notification.

Basis: 40 CFR 262.13–262.17; EPA generator summary

6. Manage containers and prevent secondary releases

By the end: Check condition, compatibility, labels, dates and the actual inspection and response arrangements.

Use containers compatible with the waste and in good condition. Keep them closed during accumulation except as the applicable rule permits. Do not handle or store them in ways that cause rupture or leakage. Separate incompatible wastes and protect them from ignition or reaction sources.

Central accumulation containers require the applicable Hazardous Waste wording, hazard indication and accumulation-start date. Satellite requirements differ in specific respects; follow the actual area’s rules. Labels must remain readable and linked to the waste determination.

Small and large quantity generator central container areas generally require at least weekly inspections for leaks and deterioration. Document and correct problems under the facility procedures and applicable rules. A checklist alone does not repair a leaking drum.

Only trained and authorized personnel perform transfers, overpacking or spill control. A leaking container may create an emergency beyond an ordinary handler’s role. Alert the designated coordinator and follow the site response plan rather than reaching into an unknown release.

Basis: 40 CFR 262.15–262.17; 1910.120(j)

7. Meet RCRA training and contingency duties

By the end: Verify the actual role-based RCRA training, supervision, annual review and contingency arrangements.

Large quantity generator personnel need role-relevant hazardous-waste management and emergency training directed by a person trained in hazardous-waste management. The program can use classroom, online or on-the-job instruction, but must teach the actual duties and contingency arrangements.

Complete the required LQG training within six months of employment or relevant assignment, whichever is later under the rule, and do not work unsupervised before completion. Personnel take part in an annual review. Maintain job titles/descriptions, training descriptions and completion evidence; current-personnel records remain until facility closure and former-personnel records at least three years after last work there.

Small quantity generators must ensure employees are thoroughly familiar with proper waste handling and emergency procedures relevant to their responsibilities. Do not automatically substitute LQG timing for SQG obligations. TSD facilities have their own training and contingency requirements under Parts 264/265 and HAZWOPER paragraph (p).

HAZWOPER training does not automatically cover all RCRA duties. The specific LQG provision avoiding duplicate emergency training for qualifying (p)(8)/(q) instruction still requires the overall facility program to meet its conditions. This awareness companion alone is not that complete facility training.

Basis: 40 CFR 262.16(b)(9); 262.17(a)(7); Part 262 Subpart M; 264.16; 265.16

8. Track manifests and verify the receiving facility

By the end: Verify shipment authorization, current facility acceptability and receiving confirmation.

Where required, hazardous waste moves with the proper manifest, EPA identification information, accurate waste description and qualified transporter and designated facility. Hazardous-materials transportation has separate DOT classification, packaging, marking, documentation and training requirements. This course does not qualify a hazmat shipping employee.

Use the current manifest/e-Manifest procedures applicable to the shipment and jurisdiction. Under current federal 262.42, an LQG missing receiving confirmation follows up with the transporter or facility at forty-five days and submits the required exception report at sixty days. SQGs also have a sixty-day missing-confirmation reporting requirement. Since December 1, 2025, the specified LQG/SQG reports go through e-Manifest; the rule has a separate submission provision for normally very-small generators using episodic-generation rules. Check state requirements and rejected-load provisions. A paid transport invoice does not prove delivery.

CERCLA off-site transfers have an additional Off-Site Rule. Covered CERCLA waste can include hazardous substances, pollutants or contaminants that are not RCRA hazardous waste. Before shipment, verify the receiving facility’s acceptability through the EPA regional process as required, as well as its authorization for the specific waste.

A facility permit alone does not prove current Off-Site Rule acceptability. The rule examines relevant violations and releases. Resolve shipment changes before loading and preserve the acceptance evidence, manifest and ultimate receipt together.

Basis: 40 CFR Part 262 Subparts B–D; 300.440

9. Recognize land-disposal and remediation-waste rules

By the end: Distinguish cleanup objectives, treatment standards and waste status before disposal.

Land Disposal Restrictions, or LDRs, can require specified treatment standards before hazardous waste is placed on the land. The standards can involve concentrations or treatment methods. Applicable notifications, certifications and records accompany the waste-management decision.

Dilution is not a substitute for required treatment where prohibited by the LDR rules. Mixing contaminated material with clean material to obtain a lower number can create additional waste and regulatory problems. Do not choose a treatment method or certify compliance outside your role.

Contaminated environmental media require careful evaluation. Listed-waste contamination, contained-in determinations, area-of-contamination policy and special remediation units can affect management, but they are not automatic exemptions. EPA or the authorized state’s applicable decisions and conditions matter.

Treatment residues and decontamination wastes may remain hazardous. Meeting a site cleanup target, an LDR treatment standard and a receiving facility’s acceptance criterion are different findings. Keep each determination and its supporting evidence separate in the project records.

Basis: 40 CFR Part 268; EPA remediation-waste guidance

10. Recognize release reporting duties

By the end: Use the emergency chain promptly and identify all required regulatory notification recipients.

CERCLA generally requires the person in charge to notify the National Response Center immediately upon knowledge of a nonexempt release of a listed hazardous substance at or above its reportable quantity in a twenty-four-hour period. The NRC number is 800-424-8802. The twenty-four-hour period is a quantity window, not permission to wait a day before reporting.

EPCRA can also require immediate notice to the State or Tribal Emergency Response Commission and Local or Tribal Emergency Planning Committee for covered releases, followed by the required written follow-up. Evaluate its scope and exceptions separately. Notification to one agency does not automatically notify every other required recipient.

Site workers promptly report observations through the emergency chain and take their assigned protective actions. The responsible person evaluates substance, quantity, pathway, time and applicable reporting duties without delaying required notice while collecting a perfect dataset. Do not put yourself at risk to estimate a release.

Cleanup-site status is not a blanket release-reporting exemption. Additional state, local, permit, oil-release or other reporting may apply. Maintain current contacts, alternates and a call record in the site plan. Emergency medical/fire calls and regulatory notification have different purposes.

Basis: 40 CFR 302.4–302.6; Part 355 Subpart C; EPA reporting guidance

11. Control water, air and special wastes

By the end: Identify every affected environmental medium and specialized material before selecting a control or outlet.

Cleanup can create contaminated runoff, pumped groundwater, dust and vapors. Determine applicable discharge and emission requirements before starting the process. Clear-looking water and low worker air results do not establish environmental compliance.

Direct discharges, sewer discharges and stormwater have different requirements. Use the applicable permit, pretreatment authorization or qualifying CERCLA substantive-compliance arrangement. Do not route decontamination water into a storm drain or sewer because it is convenient.

Asbestos, PCBs and other specialized materials can trigger separate programs. PCB remediation waste under TSCA Part 761 has specific cleanup/disposal pathways and associated sampling, notification, approval or record conditions depending on the pathway. A general RCRA determination does not eliminate TSCA duties.

For asbestos demolition or renovation, evaluate NESHAP and applicable accreditation and state rules; use the separate asbestos courses and qualified personnel. Current substance-specific requirements must be checked for the actual contaminants. This companion is an identification and escalation course, not a complete permit-design or specialized-remediation qualification.

Basis: 40 CFR Parts 122, 403, 761; Part 61 Subpart M; controlling cleanup documents

12. Verify environmental completion and continuing duties

By the end: Use actual evidence and approval conditions to close work and assign continuing responsibilities.

Before declaring a cleanup complete, compare actual work with the approved objectives and documentation requirements. Qualified personnel evaluate confirmation samples, data quality, remaining contamination, treatment performance and agency acceptance where required. A clean-looking excavation is not the completion criterion.

Some sites retain caps, monitoring wells, treatment systems or institutional controls such as use restrictions. Record who maintains them, inspection schedules, reporting, access restrictions and what triggers further work. Waste removal does not necessarily mean unrestricted property use.

Preserve waste determinations, manifests and receipts, treatment records, reports, approvals and training evidence under their applicable retention rules. Different records have different periods; do not apply one short retention period to the whole project. Keep private medical information separate.

The employer must also verify worker readiness independently: required training and field experience, medical and respiratory arrangements, site briefing and assigned role. This course’s score documents knowledge only. Resolve open environmental and occupational actions before authorizing the next phase or closing the project.

Basis: 40 CFR Part 300; 262.11, 262.40; controlling orders, permits and plans

Sources

Federal OSHA and EPA sources reviewed October 22, 2026. Confirm the actual work, jurisdiction and applicable additional requirements. Agency guidance supports planning; it is distinguished from mandatory standard text.