Universal Waste Rules: Batteries, Lamps, Aerosol Cans, and Jobsite Storage

An electrical contractor removes 200 fluorescent tubes during a warehouse retrofit. A maintenance crew collects spent lithium-ion tool batteries. A painting subcontractor has several hazardous aerosol cans with blocked nozzles and leftover product. All three waste streams may qualify as universal waste. But their classification, storage requirements, and shipping arrangements depend on the material, its condition, and the state where it is managed.

Federal 40 CFR Part 273 establishes streamlined management standards for certain commonly generated hazardous wastes. Qualifying universal waste can generally accumulate for up to one year, and ordinary universal-waste shipments do not call for a conventional federal hazardous-waste manifest. These provisions simplify certain RCRA obligations. They do not allow businesses to freely treat, dilute, crush, shred, puncture, or dispose of universal waste. States may impose additional requirements. Washington has a separate lamp threshold and indoor-storage requirements. Texas recognizes qualifying hazardous paint-related wastes. California imposes specific requirements for aerosol cans, employee training, shipment records, and photovoltaic modules.

Before selecting a universal-waste management pathway, confirm that the material qualifies and that the applicable state recognizes the category. This guide explains the federal requirements, differences in selected state programs, and practical procedures for construction contractors, maintenance companies, warehouses, and industrial facilities. For ordinary hazardous-waste generator categories, manifests, and accumulation requirements, see HazComFast's Hazardous Waste Disposal Requirements: OSHA & EPA Compliance Guide.

What is universal waste under RCRA?

Universal waste is a defined category of hazardous waste managed under alternative standards established through the Resource Conservation and Recovery Act (RCRA). Federal Part 273 covers five categories.

Not every discarded battery, lamp, or aerosol can qualifies.

Three questions determine eligibility

1. Has the material become waste? Used products generally become waste when discarded. Unused products may become waste when the holder decides to discard them. Some categories, including recalled pesticides, have additional waste-generation provisions.
2. Is it hazardous waste? Federal universal-waste eligibility generally depends on the material meeting the applicable hazardous-waste criteria. The generator needs to make an appropriate hazardous-waste determination under 40 CFR 40 CFR 262.11.
3. Does the applicable jurisdiction recognize the category? Authorized states may have different adoption, exclusions, or additional waste categories. Federal eligibility does not establish that every state permits the same management approach.

Is recycling compulsory?

Federal Part 273 encourages collection and recycling but does not generally call for all universal wastes to be recycled. Eligible universal waste may be sent to an appropriate destination facility for recycling, treatment, or disposal. However, universal-waste handlers generally cannot dispose of the material themselves. A specific condition applies when handlers puncture aerosol cans under the federal Part 273 provisions: the emptied, punctured cans need to be recycled.

Regulatory references: 40 CFR Part 273, 40 CFR 273.1–273.9, 273.11, 273.31, and 273.60.

Universal-waste classification decision table

Use this table before accepting discarded materials into a universal-waste accumulation area.

A recycling label or collection contractor's marketing description does not substitute for a lawful waste classification.

What universal-waste handlers cannot do

Under 40 CFR 40 CFR 273.11 and 273.31, small and large quantity universal-waste handlers generally cannot dispose of, dilute, or treat universal waste except as expressly permitted.

A facility that shreds batteries for recycling is not simply an ordinary universal-waste handler. It needs to evaluate the applicable destination-facility, recycling, treatment, storage, and permitting requirements. References: 40 CFR 40 CFR 273.13; 40 CFR 40 CFR 273.33.

Small vs. large quantity universal-waste handlers

Federal handler classification depends on the quantity of universal waste accumulated at a site at one time.

The five federal categories are counted collectively. A site with 3,000 kg of qualifying batteries and 2,100 kg of qualifying lamps has accumulated 5,100 kg of federal universal waste. It meets the federal large-handler definition even though neither category individually reaches 5,000 kg. Once the threshold is reached, large-handler designation continues through the end of that calendar year.

EPA identification numbers

Federal small quantity handlers do not need to notify EPA solely because they handle universal waste under 40 CFR 273.12. Under 40 CFR 273.32, federal large quantity handlers generally need to complete the applicable notification and EPA identification requirements before reaching the threshold, subject to specific exceptions. States may establish additional identification requirements.

Universal-waste status is not VSQG, SQG, or LQG status

Conventional hazardous-waste generator categories depend on qualifying amounts generated during a calendar month and other criteria. Universal-waste handler categories depend on accumulated universal waste at one time. Qualifying waste managed under Part 273 generally is not counted toward ordinary hazardous-waste generator classification. A business can therefore be a small quantity universal-waste handler and separately an SQG or LQG for other hazardous waste. The federal household and very small quantity generator provisions in 40 CFR 273.8 also permit certain exempt waste streams to be voluntarily managed under Part 273. Do not assume identical exemptions in every authorized state.

Batteries: Lithium-ion, lead-acid, and damaged cells

Battery waste is common in electrical contracting, HVAC maintenance, telecommunications, warehouses, and industrial equipment servicing. The federal battery definition is based on the device's electrochemical function, rather than a particular battery size or chemistry. Federal universal-waste eligibility still depends on hazardous-waste classification and applicable exclusions.

Lithium-ion and lithium-metal batteries

EPA recognizes that many discarded lithium batteries are likely hazardous because of ignitability or reactivity.

Examples include:

• Rechargeable power-tool batteries.

• Portable inspection-equipment batteries.

• Emergency-lighting batteries.

• Batteries removed from electronic equipment.

• Certain industrial equipment batteries.

Damaged packs versus breached cells

EPA distinguishes damage to a battery pack's exterior from damage to an individual cell casing. A damaged pack may remain universal waste when individual cell casings remain intact and the other applicable conditions are met. Hazardous waste batteries with accidentally breached individual cell casings cannot continue to be managed through the ordinary universal-waste battery pathway under EPA's interpretation. They need to be managed under the applicable conventional hazardous-waste requirements.

Exception for controlled electrolyte removal

Federal 40 CFR 273.13(a)(2) and 273.33(a)(2) expressly permit certain battery-management operations while requiring individual cell casings to remain intact and closed, except that cells may be opened to remove electrolyte and needs to be immediately closed afterward. That is a narrow, controlled exception. It does not authorize uncontrolled damage, crushing, shredding, or ordinary opening of lithium cells by unqualified personnel. The handler needs to determine whether removed electrolyte and other resulting material are hazardous waste and manage them accordingly.

A regulatory permission to remove electrolyte is not a recommendation to perform that activity on lithium-ion batteries at a construction site.

Containment requirements

Universal-waste batteries showing leakage, spillage, or damage capable of causing leakage under reasonably foreseeable conditions need to be contained.

The container needs to be:

• Closed.

• Structurally sound.

• Compatible with the battery contents.

• Free from damage likely to cause releases.

EPA-recommended precautions

EPA recommends:

• Protecting terminals against short circuits.

• Avoiding crushing and puncturing.

• Separating damaged or defective batteries.

• Selecting suitable storage conditions.

• Planning for thermal-runaway and fire emergencies.

• Coordinating significant battery hazards with emergency responders.

These recommendations do not establish one universal federal storage temperature or separation distance. Other laws, including DOT regulations and applicable fire codes, may impose specific requirements.

Transporting damaged lithium batteries

DOT requirements need to be evaluated separately from RCRA waste classification. Under 49 CFR §173.185(f), lithium batteries that fall within its damaged, defective, or recalled classification may be transported by highway, rail, or vessel only.

The provision establishes specific packaging conditions, including:

• Individual nonmetallic inner packaging.

• Noncombustible, electrically nonconductive, absorbent cushioning.

• Authorized outer packaging meeting the specified Packing Group I performance requirements.

• Needed markings identifying damaged or defective lithium batteries.

Air transportation is prohibited for lithium batteries covered by §173.185(f). A contractor should obtain the appropriate hazardous-material transportation classification and packaging arrangements rather than improvising a shipping container. The mere fact that a battery remains eligible under RCRA's universal-waste rules does not eliminate these DOT restrictions.

Official DOT reference: 49 CFR §173.185.

Spent lead-acid batteries

Spent lead-acid batteries being reclaimed may be managed under 40 CFR Part 266, Subpart G. Under 40 CFR 273.2, batteries managed through that alternative are excluded from Part 273. Eligible spent lead-acid batteries may instead follow Part 273 when its conditions are met. The actual management pathway determines the requirements.

EPA guidance: Lithium-Ion Battery Recycling Frequently Asked Questions.

Lamps: Storage, breakage, and mercury risks

Certain discarded fluorescent lamps, compact fluorescent lamps, mercury-vapor lamps, and high-intensity discharge lamps may qualify as universal waste. A lamp is not automatically hazardous solely because it is fluorescent, and low-mercury marketing does not conclusively establish that it is nonhazardous.

Federal packaging requirements

Under 40 CFR 273.13(d) and 273.33(d), qualifying universal-waste lamps need to be accumulated in containers or packages that:

• Are structurally sound.

• Are compatible with the waste.

• Protect against breakage.

• Remain closed.

• Have no damage likely to cause releases.

Properly sized protective lamp cartons are generally appropriate for lighting replacement projects.

Accidentally broken lamps

EPA confirms that accidentally broken hazardous lamps may remain universal waste under the federal program when immediately cleaned up and properly contained. Broken material needs to be placed into suitable closed packaging that prevents releases. This does not authorize routine intentional lamp crushing.

State requirements for crushing or processing need to be evaluated separately.

Additional Washington lamp-storage requirement

Washington has a specific indoor-storage rule under WAC 173-303-573. Both small and large quantity handlers need to store universal-waste lamps accumulated in cardboard or fiber containers indoors, inside a structure that prevents exposure of the container to the elements. This is a binding Washington requirement, not merely a recommendation to keep lamp boxes dry. A covered outdoor pallet or temporary tarpaulin should not automatically be treated as satisfying the requirement. The site needs to evaluate whether the actual structure prevents exposure as the regulation calls for.

Washington source: WAC 173-303-573.

Aerosol cans: Eligibility, storage, and puncturing

Federal Part 273 includes qualifying discarded hazardous aerosol cans. Examples include certain aerosol coatings, adhesives, lubricants, cleaners, and pesticides.

Empty versus nonempty cans

Federal 40 CFR 273.6 excludes cans that:

• Have not become waste.

• Are not hazardous waste.

• Meet the federal empty-container standard in 40 CFR 261.7.

A can that no longer sprays is not automatically empty. A clogged nozzle or exhausted propellant can leave hazardous product inside.

Federal aerosol storage

Under 40 CFR 273.13(e) and 273.33(e), qualifying aerosol cans need to be accumulated in suitable, compatible, structurally sound containers protected from heat sources. Leaking cans call for appropriate containment, overpacking, or authorized puncturing and draining.

Puncturing and draining

Federal Part 273 permits handlers to puncture and drain qualifying aerosol cans only under detailed conditions.

These include:

1. Equipment specifically designed to safely puncture cans and contain their contents and emissions.

2. Written operating procedures.

3. Manufacturer specifications and instructions available on site.

4. Employee training.

5. Controls preventing fire and environmental releases.

6. Appropriate ventilation and equipment placement.

7. Immediate transfer of collected contents to appropriate containers or tanks meeting applicable Part 262 requirements.

8. A hazardous-waste determination under 40 CFR 262.11.

9. Management of hazardous collected residues under conventional hazardous-waste requirements.

10. Written spill procedures and suitable cleanup materials.

11. Recycling the emptied, punctured cans.

The handler becomes the generator of hazardous waste produced by the puncturing operation. Drained hazardous liquids do not remain universal-waste aerosol cans. For occasional discarded cans, compliant off-site collection may be simpler than operating an on-site puncturing process. This is an operational recommendation, not an EPA requirement.

Reference: 40 CFR 40 CFR 273.13(e).

Pesticides and mercury-containing equipment: Needed handling controls

These two federal universal-waste categories have specific containment and handling conditions that should not be overlooked.

Universal-waste pesticides

Under 40 CFR 273.3, only certain pesticides qualify, principally specified recalled pesticide stocks and unused pesticide products collected under qualifying programs. Ordinary unwanted pesticides do not automatically meet those criteria.

Federal pesticide containment options

Section 273.13(b), with corresponding large-handler requirements in 40 CFR 273.33(b), calls for management that prevents releases.

Permitted containment arrangements include:

The appropriate option depends on the actual pesticide waste and its container. Pesticide universal-waste labeling also calls for applicable product-label information or permitted alternatives in addition to universal-waste identification. A pesticide waste that does not qualify under 40 CFR 273.3 needs to be evaluated under other applicable hazardous-waste requirements.

Reference: 40 CFR 40 CFR 273.13(b).

Mercury-containing equipment

The federal category covers qualifying hazardous devices in which elemental mercury is integral to the device's function. Examples include certain thermostats, switches, relays, and measuring instruments. Under 40 CFR 273.13(c) and 273.33(c), handlers need to manage the equipment to prevent mercury releases. Equipment with exposed elemental mercury, leakage, or damage capable of causing releases need to be placed into suitable containment. The container needs to also be designed to prevent mercury escaping through volatilization or other means.

Removing mercury-containing ampules

Federal law conditionally permits removing mercury-containing ampules from eligible equipment.

The requirements include:

• Preventing ampule breakage.

• Conducting removal over or inside appropriate containment.

• Having a mercury cleanup system readily available.

• Immediately transferring spilled mercury into compliant waste containment.

• Providing appropriate ventilation.

• Monitoring the work area to ensure compliance with applicable OSHA mercury exposure limits.

• Ensuring workers performing removal are thoroughly familiar with mercury-handling and emergency procedures.

• Storing removed ampules in suitable closed, nonleaking containers.

• Using protective packaging to prevent breakage.

The handler needs to evaluate mercury residues, cleanup waste, and other materials generated during removal. If those materials exhibit a hazardous-waste characteristic, conventional hazardous-waste requirements apply.

Practical decision

For ordinary maintenance operations, keeping mercury devices intact until shipment may be preferable to dismantling them. That is a recommended risk-control approach, not a prohibition on all authorized component removal.

Reference: 40 CFR 40 CFR 273.13(c).

Accumulation time and labeling

Federal one-year limit

Under 40 CFR 273.15 and 273.35, small and large quantity handlers generally may accumulate universal waste for no longer than one year from the date it is generated or received from another handler. The handler needs to be able to demonstrate the accumulation period.

Acceptable methods include:

• Dating individual waste items.

• Marking containers with the earliest accumulation date.

• Maintaining an appropriate on-site inventory.

• Identifying the earliest date for a group of containers or accumulation area.

• Using another method that clearly establishes the waste's age.

A date is not needed on every individual item if another permitted method satisfies the rule.

Limited exception

Longer accumulation is allowed when it is solely necessary to accumulate sufficient quantities to facilitate proper recovery, treatment, or disposal. The handler bears the burden of demonstrating that the exception applies. Ordinary scheduling delays or forgotten waste should not automatically be treated as qualifying reasons.

Labeling examples

Federal 40 CFR 273.14 and 273.34 establish acceptable category-identification wording.

Other permitted wording includes certain alternatives such as "Used Lamps" and "Waste Batteries."

Example jobsite label

UNIVERSAL WASTE, LAMPS

Contents: Spent fluorescent tubes

Earliest accumulation date: April 15, 2026

Storage location: Maintenance Room B

Handling note: Keep closed; protect against breakage

The category identification needs to meet the applicable legal requirement. The additional tracking fields are recommended unless a separate provision calls for them.

Jobsite storage and contractor responsibilities

Construction and maintenance jobsites often generate universal waste at temporary locations. Several subcontractors may generate different waste streams while a property owner or general contractor controls the collection area.

Before work begins, identify who will:

• Determine waste eligibility.

• Supply appropriate containers.

• Label or mark waste.

• Track accumulation quantities and dates.

• Respond to damaged containers or releases.

• Arrange transportation.

• Verify receiving facilities.

• Maintain needed records.

EPA has recognized that both property owners and contractors can have generator or handler responsibilities when hazardous lamps are removed during renovation. A contractual assignment does not automatically eliminate legal responsibilities arising from actual activities.

Setting up the collection area

These recommendations do not establish a universal federal storage-room design, prescribed temperature, or inspection interval. Applicable fire codes, DOT provisions, OSHA requirements, and state rules may impose additional controls.

A practical jobsite procedure

1. Before waste generation: Identify expected waste types, containers, responsibilities, and receiving facilities.
2. When waste is generated: Determine its classification and place it into the appropriate collection system.
3. During accumulation: Check container condition, labels, waste quantities, and accumulation age.
4. Before shipment: Verify the receiving facility, shipping classification, packaging, state requirements, and records.
5. After shipment: Retain needed documentation and reconcile the inventory.

Multiple jobsites

Federal handler classification is generally tied to the relevant site, including contiguous property under the applicable definition. Separate, noncontiguous jobsites are not automatically combined for the federal 5,000 kg threshold. However, a separate consolidation warehouse receiving universal waste from several projects need to evaluate its own handler status and shipment obligations. Movement between legally distinct locations may constitute an off-site shipment, even when the locations have the same owner.

Employee training and release response

Federal small quantity handlers

Under 40 CFR 273.16, employees who handle universal waste or are responsible for its management need to be informed about the proper handling and emergency procedures appropriate to the waste types.

Federal large quantity handlers

Under 40 CFR 273.36, relevant employees need to be thoroughly familiar with waste-handling and emergency procedures relative to their responsibilities. Federal Part 273 does not establish a universal annual refresher-training interval.

State regulations or separate DOT and OSHA provisions may impose additional duties.

Releases and cleanup

Under 40 CFR 273.17 and 273.37, handlers need to immediately contain releases of universal waste and associated residues. They need to determine whether material generated by the release is hazardous waste. Hazardous residues that no longer qualify as universal waste need to be managed under the applicable conventional hazardous-waste requirements. Workers should not perform cleanup beyond their training, equipment, or emergency-response authorization.

Shipping universal waste

Federal Part 273 generally allows qualifying universal waste to be sent to another appropriate universal-waste handler, a destination facility, or a foreign destination under the applicable requirements. Before shipping to another handler, the originating handler needs to ensure that the receiving handler agrees to accept the waste.

Hazardous-waste manifests

Qualifying federal universal-waste shipments generally do not call for a conventional hazardous-waste manifest. However, DOT hazardous-material requirements may apply independently.

Federal handler shipment records

Large quantity handlers need to keep the incoming and outgoing records prescribed by 40 CFR 273.39. These include relevant names and addresses, quantities by waste type, and shipment dates.

Rejected shipments

Sections 273.18 and 273.38 establish requirements for rejected shipments and improperly received hazardous waste that is not universal waste. Handlers need to follow the applicable return, alternative-destination, and notification procedures.

Transportation

Universal-waste transporters are subject to Part 273, Subpart D, and applicable DOT requirements. Under 40 CFR 273.53, a transporter may hold universal waste at a transportation-related transfer facility for ten days or less. Longer storage makes the transporter subject to the relevant handler standards while the material is stored.

Handlers, transporters, recyclers, and destination facilities

The responsibilities of the participants in the universal-waste system are different.

Destination facilities are not ordinary handlers

Under 40 CFR 273.60, destination facilities need to comply with applicable hazardous-waste treatment, storage, disposal, recycling, and permitting provisions. A facility that stores hazardous waste before recycling may call for a RCRA storage permit, unless another specific regulatory provision applies. A facility recycling without prior storage is governed by the applicable requirements of 40 CFR 261.6(c)(2). Recycling activity does not automatically exempt a facility from hazardous-waste storage requirements.

Needed destination-facility shipment records

40 CFR 40 CFR 273.62 imposes a separate recordkeeping requirement on destination facilities. The owner or operator needs to keep a record of each universal-waste shipment received.

The record needs to identify:

1. The name and address of the originating universal-waste handler, destination facility, or foreign shipper.

2. The quantity of each type of universal waste received.

3. The date the shipment was received.

The record may be maintained as a log, invoice, manifest, bill of lading, movement document, or another appropriate shipping record. The destination facility needs to retain the record for no less than three years from the date of receipt. This obligation is separate from the incoming and outgoing shipment records needed of large quantity handlers under 40 CFR 273.39.

Comparison of federal tracking duties

Regulatory references: 40 CFR 40 CFR 273.62; 40 CFR 40 CFR 273.60; 40 CFR 40 CFR 261.6.

California: Training, small-generator exemptions, and shipment records

California regulates universal waste under Title 22, Division 4.5, Chapter 23, along with additional statutory requirements.

Annual training for covered personnel

Under 22 CCR §66273.36, covered personnel who manage universal waste and their supervisors generally call for initial and annual training, subject to applicable exemptions. Covered activities include sorting, consolidating, treating, packaging for shipment, offering waste for shipment, and physically relocating universal-waste containers. Employees whose normal duties are limited to generating universal waste and depositing it into designated collection areas are not automatically considered personnel who manage universal waste for this provision. Dated training records generally need to be retained for no less than three years after the individual last managed universal waste at the facility.

California very small quantity universal-waste generators

Under 22 CCR §66273.9, the definition of a very small quantity universal-waste generator includes the following criteria:

The exemption in §66273.8 is conditional. A company does not qualify simply because it has few employees or a small universal-waste collection bin. Important: California Health and Safety Code §25201.16(d)(2) excludes hazardous universal-waste aerosol cans from the general household and very small universal-waste generator exemptions. Use the inclusive boundaries in 22 CCR §66273.9: no more than 100 kg and no more than 1 kg. The exemption also depends on the conditions in §66273.8 and the federal conditions incorporated by the definition.

California shipment tracking

Under 22 CCR §66273.39, universal-waste handlers generally need to maintain incoming and outgoing shipment records, subject to applicable exemptions and special provisions. Needed information includes relevant names and addresses, quantities by waste type, and shipment dates. Records need to generally be retained for no less than three years. This differs from the federal small-handler rule in 40 CFR 273.19.

California identification for non-RCRA universal waste

Under 22 CCR §66273.32(b), a handler accumulating 5,000 kg of universal waste that does not trigger the corresponding federal notification requirement because it is hazardous only under California law needs to obtain the applicable California identification number. Other California identification obligations may apply independently.

Official guidance: California DTSC Universal Waste Fact Sheet.

California aerosol cans and photovoltaic modules

Hazardous aerosol cans

California Health and Safety Code §25201.16 establishes additional management requirements for hazardous nonempty aerosol cans. An aerosol can may become waste when discarded or no longer usable, including when its spray mechanism is blocked or damaged or its propellant has been exhausted. A can that no longer sprays is not automatically empty. California's aerosol-specific empty-container criteria are found in 22 CCR §66261.7(m).

California HSC §25201.16 also establishes storage conditions relating to container strength, compatibility, heat, pressure, ventilation, labeling, and incompatible materials. Under specific conditions, certain pre-processing or pre-shipment accumulation containers may remain open during the workday if covered at the end of the day. That exception does not remove the other fire and release-prevention duties. For handlers conducting qualifying aerosol processing, the applicable notification to the CUPA or other authorized agency needs to be made by the day processing begins. Relevant changes generally call for an amended notification in 30 days or less.

Official source: DTSC Aerosol Can Waste Management.

California photovoltaic modules

California recognizes qualifying hazardous photovoltaic modules under its state universal-waste program. Under 22 CCR §66273.7.1, the pathway generally concerns discarded modules hazardous solely because of the specified toxicity characteristic. Modules exhibiting disqualifying hazardous characteristics do not automatically qualify. Several notification and reporting requirements need to be distinguished.

These annual activity thresholds are not the same as the federal large-handler threshold based on accumulated quantities at one time. For qualifying activity during calendar year 2026, the annual reporting deadline is February 1, 2027.

Official guidance: DTSC Photovoltaic Module Regulations.

Washington, Texas, and ohio: State differences

Washington

Washington's universal-waste program is established under WAC 173-303-573. It covers batteries, mercury-containing equipment, and lamps. It does not include the federal pesticide or aerosol-can categories. Washington also has a lamp-specific large-handler threshold.

Under WAC 173-303-040, the large-handler definition includes:

• 11,000 pounds or more of total qualifying universal waste; or

• More than 2,200 pounds of universal-waste lamps.

The notification provision uses a different boundary: WAC 173-303-573(19) calls for the notification and EPA identification number before meeting or exceeding 11,000 pounds total or 2,200 pounds of lamps, unless the existing-notification exception applies. Plan notification before reaching 2,200 pounds of lamps even though the lamp-specific large-handler definition says more than 2,200 pounds. Indoor lamp storage: Both small and large handlers need to keep lamps accumulated in cardboard or fiber containers inside a structure protecting the containers from the elements.

Official regulation: WAC 173-303-573.

Texas

Texas recognizes qualifying hazardous paint and paint-related wastes under 30 TAC §335.262. The category does not automatically include every discarded paint product, solvent, or paint container. Eligibility depends on the actual definitions and requirements. Under §335.262(d), hazardous-waste determinations made pursuant to subsection (b) needs to be documented when made and retained for no less than three years. This is a binding documentation obligation. The rule also establishes container, labeling, and compatibility requirements, including special controls for ignitable, reactive, and incompatible wastes.

The prescribed category identification includes:

Universal Waste - Paint and Paint-Related Wastes

Official agency: Texas TCEQ Universal Waste Guidance.

Ohio

Ohio's program appears in Ohio Administrative Code Chapter 3745-273. Updated rules effective January 16, 2026, recognize the federal categories plus qualifying antifreeze and paint-related wastes. Ohio counts the recognized categories collectively for its handler threshold. Under OAC 3745-273-09, a universal-waste aerosol satellite accumulation area is defined as a designated container or unit with a capacity not exceeding 55 gallons, or a designated cabinet, where aerosol cans are initially collected in the work area. This is an Ohio-specific definition, not a nationwide federal aerosol storage limit.

Official regulation: Ohio Rule 3745-273-09.

Selected state comparison

For an interstate shipment, check the origin, transit, and destination states; recognition of a category in one state does not establish its status elsewhere.

Interstate shipment example: Ohio to Washington

An Ohio contractor accumulates hazardous paint-related material qualifying under Ohio's universal-waste rules. The contractor plans to ship it to Washington. Ohio recognizes certain hazardous paint-related wastes as universal waste. Washington does not include that category in its universal-waste program. The Ohio classification therefore does not automatically authorize the same management pathway in Washington.

Before shipping, the contractor needs to determine:

1. Whether the waste is federally hazardous.

2. Whether Washington regulates it as dangerous waste.

3. Whether another lawful exemption or pathway applies.

4. Whether the receiving facility may legally accept the material.

5. Which generator, transporter, manifest, and DOT requirements apply.

6. Whether transit-state rules affect the shipment.

Where the receiving state does not recognize a state-only category, conventional hazardous-waste requirements may apply if the material is hazardous and no other lawful pathway is available. Recommended practice: Obtain written classification and acceptance confirmation from the receiving facility before dispatch.

Reference: EPA State Universal Waste Programs.

Hypothetical Texas jobsite inventory

A Texas maintenance contractor completes a warehouse retrofit. The quantities below are hypothetical and are used solely to illustrate classification and inventory decisions.

The four federal universal-waste streams total:

130 + 80 + 16 + 8 = 234 kg. Including the 25 kg of qualifying Texas paint-related waste produces an illustrative combined universal-waste inventory of 259 kg, subject to the applicable Texas counting rules. Both figures are below 5,000 kg. The spent lead-acid batteries managed under the Part 266 reclamation pathway are not automatically Part 273 universal waste. The hazardous solvent needs to be evaluated independently for conventional hazardous-waste generator status. If the Texas paint-related universal-waste pathway applies, its needed waste determination needs to be documented and retained under §335.262(d).

The receiving facilities, shipping requirements, and transportation documentation need to be established before waste leaves the project.

Universal-waste compliance inspection checklist

Use this checklist during routine inspections and pre-shipment reviews.

Ready-to-use record templates

These templates can be adapted for a workplace waste-management program. Not every field is needed by federal Part 273.

Template A: Universal waste accumulation log

Regulatory purpose: An appropriately maintained inventory can demonstrate accumulation age under 40 CFR 273.15 and 273.35.

Additional fields are operational recommendations unless separately needed.

Template B: Universal waste shipment record

Federal large quantity handler: Needed records under 40 CFR 273.39 need to be retained for no less than three years. Federal destination facility: Records for each incoming universal-waste shipment under 40 CFR 273.62 need to be retained no less than three years after receipt. California handler: Incoming and outgoing shipment tracking is generally needed under §66273.39, subject to applicable exemptions.

Template C: Waste classification and acceptance record

Facility:

State:

Material description:

Assessment date:

Responsible person:

Selected regulatory pathway:

Applicable citation:

Supporting evidence:

Outstanding corrective actions:

Approval/date:

For Texas paint-related determinations covered by §335.262(d), specific documentation and retention requirements apply.

Template D: California universal-waste training record

For covered personnel under §66273.36, records generally need to be retained for no less than three years after the individual last managed universal waste at the facility. Separate DOT documentation may also be needed.

Regulatory sources

Federal regulations and EPA guidance

• 40 CFR Part 273, Universal Waste Management

• 40 CFR 40 CFR 273.13, Waste Management

• 40 CFR 40 CFR 273.39, Large-Handler Shipment Tracking

• 40 CFR 40 CFR 273.60, Destination Facilities

• 40 CFR 40 CFR 273.62, Destination-Facility Shipment Records

• 40 CFR 40 CFR 261.6, Hazardous Waste Recycling

• 40 CFR 40 CFR 262.11, Hazardous Waste Determination

• 40 CFR Part 266, Specific Waste Management Standards

• 49 CFR §173.185, Lithium Battery Transportation

• EPA Universal Waste Program

• EPA Universal Waste FAQs

• EPA Lithium-Ion Battery Recycling FAQs

• EPA State Universal Waste Programs

California

• DTSC Universal Waste Fact Sheet

• DTSC Aerosol Can Waste Management

• DTSC Photovoltaic Module Regulations

• 22 CCR §66273.32, California notification and PV reporting

• 22 CCR §66273.36, California personnel training

• Other applicable California provisions: §§66273.8, 66273.9, 66273.39, 66273.74, and 66261.7(m).

• California Health and Safety Code §25201.16, aerosol cans.

Other states

• Washington WAC 173-303-040

• Washington WAC 173-303-573

• Texas TCEQ Universal Waste Guidance

• Ohio Rule 3745-273-09

This guide summarizes federal requirements and selected state-specific differences. It is not a complete audit of all state programs. Requirements should be confirmed for the waste, facility, activity, and destination involved.