Identify the PCB material category

Distinguish PCB liquids, transformers, capacitors, articles, bulk product waste, remediation waste, spill cleanup waste, fluorescent-light ballasts, and contaminated media. Preserve source and concentration data.

Define the legal pathway

Apply the specific use, storage, cleanup, decontamination, or disposal provision. PCB remediation waste decisions can involve self-implementing cleanup, performance-based disposal, risk-based approval, or other authorized options.

Control storage and movement

Use compatible containment, required markings, inspections, dates, manifests or records where applicable, spill control, and approved commercial storage or disposal facilities. Avoid mixing that changes volume or complexity.

Worked example: old transformer leak

A facility secures the area, identifies equipment and PCB concentration records, prevents migration, evaluates spill-cleanup requirements, characterizes affected surfaces and debris, and selects an authorized disposal route.

Document completion

Retain inventories, analytical data, photographs, cleanup levels, notifications or approvals, shipping records, certificates, annual records, and closure evidence as applicable.

Put the requirement into daily work

Assign an accountable owner and translate the PCB waste management TSCA decision into a field standard. Identify who performs each step, who reviews exceptions, what training and equipment are required, and where evidence is retained. Test the workflow with a real facility example before broad use.

Connect environmental, operations, maintenance, laboratory, purchasing, shipping, emergency-response, and contractor roles where their decisions affect the outcome. Use clear acceptance criteria so the same facts produce the same decision.

Records and reevaluation triggers

Keep the current regulatory basis, facility analysis, approvals, operating records, and exception history under a stable identifier. A reviewer should be able to reconstruct what was known, who decided, how the control was implemented, and how ongoing performance was verified.

Reevaluate after changes in material, process, equipment, quantity, storage, handling, vendor, destination, permit, law, incident, inspection finding, analytical result, or recurring failure. Document both the trigger and the resulting decision.

Common mistakes

• Assuming every oil-filled device is PCB-free.
• Using a RCRA waste code as the only PCB decision.
• Cleaning before documenting spill extent.
• Sending PCB waste to an unverified facility.
• Ignoring state PCB or spill requirements.