Safe Handling of Hazardous Drugs — Part 3: Spill Management, Waste Disposal, and Decontamination
Spill classification and step-by-step response procedures, spill kit contents, personnel exposure management during spills, hazardous drug waste segregation and disposal, and surface decontamination protocols including deactivation, decontamination, and cleaning agents.
9. Spill Management
Spills of hazardous drugs represent acute exposure events that require immediate, trained, and systematic response. Every facility that handles hazardous drugs must have written spill procedures, maintain spill kits in all areas where hazardous drugs are handled, and ensure that all personnel who might encounter a spill are trained in spill response.1
9.1 Spill Kit Contents
Spill kits must be readily accessible in every area where hazardous drugs are stored, compounded, administered, transported, or disposed of. Kits should be commercially available, pre-assembled kits specifically designed for hazardous drug spills, or institution-assembled kits containing the following components:2
| Component | Specification |
|---|---|
| Chemotherapy-tested gloves | Two pairs (for double gloving); sizes appropriate for likely users (consider stocking multiple sizes) |
| Protective gown | One disposable, chemotherapy-rated, impervious gown |
| Face shield or splash-proof goggles | One face shield or one pair of non-vented splash goggles |
| Respiratory protection | One N95 respirator (for small spills); for large spill kits, include a chemical cartridge respirator or PAPR with organic vapor/P100 cartridges |
| Shoe covers | Two pairs of disposable, impervious shoe covers |
| Absorbent pads/sheets | Plastic-backed absorbent sheets or pads sufficient to cover the spill area; chemotherapy-rated |
| Absorbent powder or granules | For liquid spills — sufficient to absorb the spill volume (some kits use absorbent pillows or towels instead) |
| Spill containment pillows or booms | For large liquid spills to contain spread |
| Disposable scoop and brush | Plastic scoop and small brush or dustpan for collecting solid material, broken glass, or absorbent material |
| Puncture-resistant container | For broken glass and sharp fragments |
| Hazardous drug waste bags | Two or more sealable, labeled HD waste bags (thick-mil plastic) |
| Decontamination solution | Pre-made or prepared sodium hypochlorite solution (0.5% or higher) or a commercially available oxidizing decontamination agent; sufficient for the area to be cleaned |
| Cleaning solution | Detergent or neutral pH cleaning solution for use after decontamination |
| Warning sign or barrier tape | To restrict access to the spill area during cleanup |
| Documentation form | Spill report/incident form for recording the event |
9.2 Spill Classification
| Spill Type | Definition | Response Level |
|---|---|---|
| Small spill | A spill involving less than 5 mL of liquid, or the contents of a single broken tablet/capsule, or a small amount of powder; contained in a limited area | Can typically be managed by the worker who discovers the spill, provided they have been trained in spill response and PPE is immediately available |
| Large spill | A spill involving 5 mL or more of liquid, or a larger quantity of powder/solid, or any spill that spreads across a wide surface area, or any spill of a volatile hazardous drug | Should be managed by designated, trained spill response personnel; may require area evacuation and enhanced respiratory protection |
| Personnel exposure spill | Any spill that results in direct skin, eye, mucous membrane, or inhalation exposure of a worker | Requires immediate first aid for the exposed worker in addition to spill cleanup; medical evaluation must follow |
9.3 Small Spill Response Procedure
Step-by-step protocol:
- Alert: Notify nearby personnel of the spill. If the spill occurs in a patient care area, move the patient (if mobile and safe to do so) away from the spill
- Restrict access: Place a warning sign or verbally restrict access to the spill area to prevent unprotected personnel from entering
- Don PPE: Put on full spill PPE from the spill kit:
- Double chemotherapy-tested gloves
- Protective gown
- Splash goggles or face shield
- N95 respirator (fit-checked)
- Shoe covers
- Contain the spill:
- For liquid spills: Place absorbent pads or sheets over the spill, working from the outer edges inward to prevent spreading. Allow the absorbent material to soak up the liquid
- For powder or solid spills: Dampen the material with water or a wet absorbent pad before attempting to collect it — this prevents further aerosolization. Use a disposable scoop to gently collect the material. Do not sweep dry powder
- For broken glass/vials: Use the disposable scoop — never pick up glass with gloved hands. Place glass fragments in the puncture-resistant container
- Decontaminate the surface:
- After removing the bulk of the spill, apply the decontamination solution (sodium hypochlorite 0.5% or equivalent) to the affected area
- Allow adequate contact time (typically 30 minutes, or per manufacturer instructions for commercial decontamination agents)
- Wipe the area with clean absorbent pads
- Apply detergent/cleaning solution and wipe again
- Rinse with water and dry
- Repeat the decontamination-cleaning cycle three times for maximum assurance
- Dispose of all materials: Place all contaminated materials (absorbent pads, gloves, gown, scoop, waste bags) in sealed HD waste bags, then into HD waste containers
- Remove PPE: Doff in the correct sequence (see Part 2, Section 8.2); perform hand hygiene
- Document: Complete the spill incident report including:
- Drug name, estimated quantity, and formulation
- Location and time of spill
- Cause of spill (if known)
- Names of personnel involved in cleanup
- Names of any personnel exposed
- PPE used during cleanup
- Decontamination procedures performed
- Corrective actions taken or recommended
9.4 Large Spill Response Procedure
Step-by-step protocol:
- Alert and evacuate: Immediately notify all personnel in the area. Evacuate non-essential personnel from the spill area. Close doors to contain potential airborne contamination
- Restrict access: Post warning signs and barrier tape to prevent entry by unprotected persons
- Notify designated spill response personnel: Contact the pharmacy, safety officer, environmental services, or other designated spill response team as defined by institutional policy
- Ventilation: If the spill involves a volatile agent or generates visible aerosol or dust:
- Turn off recirculating fans or HVAC returns in the immediate area if possible to prevent spreading contamination through the ventilation system
- Open windows to the outside (if applicable and if this creates outward airflow)
- If the spill occurs in a negative-pressure room, the room’s exhaust system will help contain airborne contamination — keep the door closed
- Don enhanced PPE: The trained spill response team must don:
- Double chemotherapy-tested gloves
- Protective gown (or chemotherapy-rated coverall for very large spills)
- Face shield
- PAPR with organic vapor/P100 cartridges, or chemical cartridge full-face respirator (N95 is the minimum if PAPR is unavailable)
- Shoe covers (impervious boot covers for large floor spills)
- Contain the spill: Use spill containment pillows or booms to prevent further spread. Then follow the absorption, collection, and decontamination steps outlined for small spills, scaling up materials as needed
- Decontaminate:
- Perform at least three cycles of decontamination-cleaning-rinse on all affected surfaces
- For carpet contamination: the contaminated section of carpet should be removed and discarded as HD waste if decontamination cannot be assured
- For upholstered furniture: if contamination cannot be removed by surface cleaning, the item should be discarded as HD waste
- Post-cleanup verification: Some institutions perform surface wipe sampling after large spill cleanup to verify adequate decontamination. While not universally required, this is a best practice for quality assurance
- Dispose and document: Per small spill protocol, with additional notation of the scale of the event, evacuation actions taken, and any facility damage
9.5 Spills on Personnel
If a hazardous drug comes into direct contact with a worker’s skin, eyes, or mucous membranes:
Skin exposure:
- Immediately remove contaminated clothing
- Wash the affected skin area with soap and water for at least 15 minutes (do not use abrasive scrubs or hot water, which may increase absorption)
- Do not use chemical neutralizing agents on skin
- Seek medical evaluation — report to occupational health or the emergency department
- Document the exposure
Eye exposure:
- Immediately flush the affected eye(s) with water or isotonic saline for at least 15 minutes using an emergency eyewash station
- Hold eyelids open during flushing to ensure thorough irrigation
- Remove contact lenses as soon as possible (if present) during flushing
- Seek immediate medical evaluation — ophthalmology consultation if significant exposure
- Document the exposure
Inhalation exposure:
- Immediately move to fresh air; leave the contaminated area
- If respiratory distress, administer supplemental oxygen and seek emergency medical care
- Report to occupational health for evaluation
- Document the exposure
Needlestick or sharps exposure with HD contamination:
- Allow the wound to bleed freely briefly; wash with soap and water
- Do not squeeze the wound aggressively
- Seek immediate medical evaluation
- Identify the specific drug(s) involved and provide this information to the evaluating clinician
- Follow institutional bloodborne pathogen exposure protocols in addition to HD-specific protocols
- Document the exposure
9.6 Spill Kits — Placement Requirements
| Location | Spill Kit Required |
|---|---|
| HD compounding area (pharmacy) | Yes — within the room or immediately outside |
| HD storage areas | Yes |
| Inpatient oncology units | Yes — at least one per unit, in a known, labeled location |
| Outpatient infusion centers | Yes — at least one per treatment area |
| Emergency department | Yes (if hazardous drugs are administered) |
| Operating rooms (where HD agents are used) | Yes |
| Shipping/receiving areas handling HDs | Yes |
| HD waste staging/holding areas | Yes |
| Transport vehicles/carts | Consideration based on assessment of risk |
10. Waste Disposal
10.1 Hazardous Drug Waste Categories
Hazardous drug waste is categorized into two types based on the amount of residual drug present. This distinction has regulatory and disposal implications.3
Trace Contamination Waste
Materials that have contacted hazardous drugs but do not contain visible or significant quantities of drug residue:
- Empty HD vials (with residual drug only in amounts that cannot be removed by common practices)
- Used gloves, gowns, shoe covers, hair covers, and other PPE
- Absorbent pads from BSC work surfaces
- Empty IV bags and tubing (with only trace residual drug remaining after administration)
- Needles and syringes used for HD administration (after drug has been administered)
- Patient care items contaminated with body fluids during the HD excretion period (diapers, linen protectors, etc.)
Trace contamination waste is classified as hazardous drug waste and must be:
- Segregated from regular medical waste and from non-HD pharmaceutical waste
- Placed in designated, clearly labeled HD waste containers (typically yellow containers with “Chemotherapy Waste” or “Hazardous Drug Waste” labeling)
- Disposed of through incineration at a permitted facility (the preferred method) or through other methods approved by the applicable environmental agency
- Sharps contaminated with HD residue must go into designated HD sharps containers, separate from regular sharps
Bulk Hazardous Drug Waste
Materials containing significant quantities of hazardous drug — including:
- Partially used vials, ampoules, or syringes with more than trace residual drug
- Unused or expired hazardous drugs
- Compounded preparations that are not administered
- IV bags or bottles returned with significant drug remaining
- Spill cleanup materials containing bulk drug
Bulk hazardous drug waste may be classified as RCRA hazardous waste (Resource Conservation and Recovery Act) if the specific drug appears on the EPA’s P-list or U-list of hazardous wastes, or if it exhibits a characteristic of hazardous waste (ignitability, corrosivity, reactivity, or toxicity per TCLP). Key examples of RCRA-listed hazardous drugs:
| EPA Waste Code | Drug |
|---|---|
| U058 | Cyclophosphamide |
| U010 | Mitomycin C |
| U045 | Chlorambucil |
| U059 | Daunomycin (Daunorubicin) |
| P050 | Arsenic trioxide |
| U237 | Uracil mustard |
| U090 | Diethylstilbestrol |
| P042 | Epinephrine (listed, but not typically handled as HD) |
| U150 | Melphalan |
| U122 | Formaldehyde (listed; relevant in some compounding contexts) |
RCRA-listed hazardous drug waste must be:
- Segregated into appropriate black RCRA hazardous waste containers
- Managed per RCRA hazardous waste generator requirements (satellite accumulation rules, 90-day/180-day storage limits, manifesting, and disposal at permitted Treatment, Storage, and Disposal Facilities)
- Never placed in regular HD (trace) waste containers or regular medical waste
Non-RCRA hazardous drug waste in bulk quantities should still be managed as hazardous drug waste and disposed of through incineration or other approved methods, though the regulatory framework may be less stringent than for RCRA waste.
10.2 Waste Container Specifications
| Container Type | Color/Label | Contents |
|---|---|---|
| HD trace waste | Yellow with “Chemotherapy Waste” or “Hazardous Drug Waste” label | PPE, empty vials, IV bags/tubing with trace drug, absorbent pads, patient care items |
| HD sharps | Yellow sharps container with HD labeling | Needles, syringes, broken vials, ampules, and other sharps contaminated with HD |
| RCRA hazardous waste | Black with appropriate RCRA labeling including waste code and accumulation start date | Bulk waste of RCRA-listed drugs; must meet EPA labeling requirements |
| Non-RCRA bulk HD waste | Managed per institutional policy; often yellow HD waste containers or separate containers per waste vendor specifications | Bulk quantities of non-RCRA-listed hazardous drugs |
10.3 Waste Handling Procedures
- Segregation at point of generation: All HD waste must be placed in the correct container immediately at the point where it is generated — do not carry HD waste to distant locations or mix with other waste streams
- PPE for waste handling: Personnel handling HD waste containers must wear at minimum double chemotherapy-tested gloves and a protective gown
- Container management:
- Do not overfill waste containers — close and replace when approximately three-quarters full
- Ensure container lids are secured when not actively depositing waste
- Inspect containers regularly for leaks or damage
- Keep waste containers in well-ventilated areas
- Transport within facility: HD waste containers must be transported in a manner that prevents tipping, breakage, or leakage (use wheeled carts with containment)
- Storage pending disposal: HD waste must be stored in designated, secure, well-ventilated areas pending pickup by the waste disposal vendor; comply with applicable storage time limits (RCRA: 90 days for large-quantity generators, 180 days for small-quantity generators)
- Documentation: Maintain waste manifests and disposal records per RCRA requirements (for RCRA waste) and per institutional policy (for non-RCRA HD waste)
10.4 Prohibited Disposal Practices
The following practices are prohibited:
- Flushing hazardous drugs down the drain or toilet (unless the specific drug’s SDS and local regulations permit this, which is rare)
- Disposing of HD waste in regular medical waste (red bag) containers
- Disposing of HD waste in regular municipal solid waste
- Compacting or grinding HD waste (may generate aerosols)
- Treating HD waste by autoclaving (does not deactivate most hazardous drugs and may generate hazardous vapors)
11. Decontamination, Deactivation, and Cleaning
The terms decontamination, deactivation, and cleaning have specific, distinct meanings in the context of hazardous drug handling. A proper surface cleaning protocol for HD-contaminated areas involves all three processes, performed in the correct sequence.4
11.1 Definitions
| Term | Definition |
|---|---|
| Deactivation | Chemical treatment that renders a hazardous drug inactive or inert. Deactivation destroys the drug molecule or reduces its toxicity. Not all hazardous drugs have validated deactivation methods |
| Decontamination | Removal or chemical inactivation of hazardous drug residues from surfaces to reduce contamination to a safe level. Often achieved using oxidizing agents that both deactivate and remove drug residues |
| Cleaning | Physical removal of organic and inorganic material (drug residue, dirt, debris) from surfaces using detergent and water. Cleaning removes residual drug that may not have been deactivated, as well as residual decontamination chemicals |
11.2 Decontamination and Cleaning Agents
| Agent | Application | Mechanism | Notes |
|---|---|---|---|
| Sodium hypochlorite (NaOCl) 2% | Deactivation and decontamination of many antineoplastic drugs | Oxidation — breaks down drug molecules through oxidative degradation | Effective against many alkylating agents, anthracyclines, and other drug classes; corrosive to stainless steel with prolonged contact — limit contact time and rinse thoroughly; do not use on aluminum surfaces |
| Sodium hypochlorite (NaOCl) 0.5% | Routine surface decontamination | Oxidation | Less corrosive than 2%; appropriate for routine daily decontamination of work surfaces |
| Sodium thiosulfate (neutralizer for bleach) | Applied after NaOCl decontamination to neutralize residual bleach before cleaning | Neutralization | Protects surface materials from bleach damage; optional step depending on surface material |
| Commercially available oxidizing surface decontaminants | Decontamination per manufacturer instructions | Various oxidizing chemistries (peracetic acid-based, peroxide-based, or proprietary formulations) | Several commercially available products have been specifically tested against panels of hazardous drugs; facility should review manufacturer’s testing data for efficacy against the drugs in use |
| Detergent/neutral pH cleaner | Cleaning step after decontamination | Physical removal of residual drug and decontamination chemicals through surfactant action | Must be applied after the decontamination agent has been allowed to dwell and has been wiped away; removes both drug residue and corrosive decontamination agents from surfaces |
| Sterile water or water for injection | Final rinse | Physical removal of cleaning agent residue | Used as final rinse in BSC/CACI cleaning to remove all chemical residues from the ISO Class 5 work surface |
11.3 Three-Step Decontamination Protocol for Surfaces
This protocol applies to all surfaces in HD handling areas, including BSC work surfaces, countertops, floors, and equipment in compounding, administration, and storage areas.5
Step 1 — Deactivation/Decontamination:
- Apply the decontamination agent (sodium hypochlorite solution or commercial decontamination product) to the surface
- Allow adequate contact time:
- Sodium hypochlorite 2%: minimum 30 minutes (or until visibly dry, then reapply and allow another contact period)
- Commercial products: per manufacturer’s instructions (typically 1–30 minutes depending on the product)
- Wipe the surface with clean, disposable towels or pads to remove the decontamination solution and any dissolved drug residue
- Discard wipes in HD waste
Step 2 — Cleaning:
- Apply detergent or neutral pH cleaning solution to the surface
- Scrub the surface to physically remove any remaining drug residue and decontamination chemical residue
- Wipe with clean, disposable towels or pads
- Discard wipes in HD waste
Step 3 — Rinse:
- Wipe the surface with clean water (sterile water for BSC/CACI work surfaces; clean tap water for floors and other surfaces)
- Dry the surface with clean, disposable towels
- Discard all materials in HD waste
11.4 Decontamination Schedule
| Surface / Area | Frequency |
|---|---|
| BSC/CACI work surface | Before and after each compounding session; after any known contamination event; at the end of each shift |
| BSC/CACI interior (walls, sash, plenum) | At least weekly; more frequently if visible contamination is detected |
| Compounding room counters and floors | Daily when compounding occurs; after any spill |
| Administration area surfaces | After each patient treatment where HD contamination may have occurred; at least daily |
| HD storage area shelves and floors | At least monthly; after any spill or breakage |
| Patient room surfaces (for patients receiving HDs) | Daily, including bed rails, overbed table, bathroom surfaces, and IV pole |
| Transport containers | After each use |
| HD waste staging areas | Weekly; after any spill or leakage |
| Equipment (infusion pumps, tubing clamps) | After each patient use; decontaminate then clean before returning to general inventory |
11.5 Surface Wipe Sampling (Environmental Monitoring)
Surface wipe sampling is a quality assurance tool used to evaluate the effectiveness of containment and cleaning practices. While not universally mandated by regulation, it is strongly recommended as a best practice and is required by some jurisdictions and accreditation bodies.6
Program elements:
| Element | Recommendation |
|---|---|
| Frequency | At least every 6 months; additionally after any significant spill, after changes in cleaning procedures, and after installation of new equipment |
| Sampling sites | BSC work surfaces, countertops in compounding areas, floor in front of BSC, pass-through windows, administration area surfaces, patient areas, door handles, telephones, and other high-touch surfaces |
| Drugs tested | Commonly assayed marker drugs include cyclophosphamide, ifosfamide, 5-fluorouracil, methotrexate, and platinum compounds (selected because validated analytical methods exist and they are commonly used) |
| Analytical method | Liquid chromatography–tandem mass spectrometry (LC-MS/MS) or equivalent validated analytical method |
| Interpretation | There is no universally accepted “safe” threshold; however, many facilities use a target of no detectable contamination or contamination below a facility-defined action level (e.g., <0.1 ng/cm² for cyclophosphamide). The trend over time is more informative than a single measurement |
| Action on positive results | Investigate the source of contamination; review handling and cleaning practices; retrain personnel if needed; repeat sampling after corrective actions to verify improvement |
References
United States Pharmacopeia. General Chapter <800> Hazardous Drugs — Handling in Healthcare Settings. Section: Spill Control. Occupational Safety and Health Administration (OSHA). “Controlling Occupational Exposure to Hazardous Drugs.” OSHA Technical Manual (OTM), Section VI, Chapter 2. U.S. Department of Labor. ↩︎
American Society of Health-System Pharmacists (ASHP). “ASHP Guidelines on Handling Hazardous Drugs.” Am J Health-Syst Pharm. 63:1172-1193, 2006. Updated 2018. Section: Spill Management and Spill Kit Contents. Oncology Nursing Society (ONS). “Safe Handling of Hazardous Drugs,” 3rd ed. Pittsburgh, PA: ONS, 2018. Chapter on Spill Management. ↩︎
Environmental Protection Agency (EPA). Resource Conservation and Recovery Act (RCRA) regulations, 40 CFR Parts 260-272. Applicable to pharmaceutical waste meeting the definition of RCRA hazardous waste. United States Pharmacopeia. General Chapter <800> Hazardous Drugs — Handling in Healthcare Settings. Section: Hazardous Drug Waste Disposal. ↩︎
United States Pharmacopeia. General Chapter <800> Hazardous Drugs — Handling in Healthcare Settings. Section: Deactivation, Decontamination, Cleaning, and Disinfection. The three-step process (deactivation/decontamination, cleaning, rinsing) is explicitly defined in USP <800>. ↩︎
International Society of Oncology Pharmacy Practitioners (ISOPP). “ISOPP Standards of Practice: Safe Handling of Cytotoxics.” J Oncol Pharm Pract. 13(Suppl):1-81, 2007. Section: Environmental Decontamination. American Society of Health-System Pharmacists (ASHP). “ASHP Guidelines on Handling Hazardous Drugs.” Am J Health-Syst Pharm. 63:1172-1193, 2006. ↩︎
Connor TH, MacKenzie BA, DeBord DG, et al. “Evaluation of antineoplastic drug exposure of health care workers at three university-based US cancer centers.” J Occup Environ Med. 52(10):1019-1027, 2010. Sessink PJ, Connor TH, Jorgenson JA, Tyler TG. “Reduction in surface contamination with antineoplastic drugs in 22 hospital pharmacies in the US following implementation of a closed-system drug transfer device.” J Oncol Pharm Pract. 17(1):39-48, 2011. Surface wipe sampling methodology and interpretation. ↩︎