Waste Management Program
Division of Environmental Quality
P.O. Box 176
Jefferson City, MO 65102-0176
United States
The Missouri Department of Natural Resources’ Waste Management Program prepared this fact sheet for Missouri businesses and institutions to help identify and manage pharmaceutical waste that is considered hazardous waste. This information should not be used in place of state or federal laws.
Note: Missouri adopted EPA’s Management Standards for Hazardous Waste Pharmaceuticals and Amendment to the P075 Listing for Nicotine (Subpart P). This rule adoption modifies regulations and management practices for hazardous waste pharmaceuticals at Healthcare Facilities and Reverse Distributors, as defined in Code of Federal Regulations 40 C.F.R. § 266.500.
To be subject to Subpart P, a facility must first be considered either a Healthcare Facility or Reverse Distributor as defined by 40 C.F.R. § 266.500:
A healthcare facility that is a very small quantity generators when counting generation of both hazardous waste pharmaceuticals and non-pharmaceutical hazardous wastes is not subject to the requirements of Subpart P, except the prohibition on sewering of hazardous waste pharmaceuticals described at 40 C.F.R. § 266.505. A healthcare facility that is a very small quantity generator as described above, who elects to not notify and operate under Subpart P, remains subject to the revised RCRA-empty standards of hazardous waste pharmaceuticals found at 40 C.F.R. § 266.507.
Healthcare facilities that are small or large quantity generators when counting generation of both hazardous waste pharmaceuticals and non-pharmaceutical hazardous wastes are subject to the requirement of Subpart P, and must notify the department of their participation. If a healthcare facility would be a lower hazardous waste generator category if counting only non-pharmaceutical hazardous waste, it may notify as such when it provides notification of compliance with Subpart P. A healthcare facility that is a small or large quantity generator when counting both hazardous waste pharmaceuticals and non-pharmaceutical hazardous wastes is still subject to Subpart P, even if the non-pharmaceutical hazardous waste total would results in a generator status change to very small quantity generator.
Pharmaceutical waste can be any of the following discarded or confiscated items:
Hazardous waste is any waste that:
Although seemingly harmless in small amounts, pharmaceutical waste can create a serious hazard to human health and the environment if disposed of incorrectly. State and federal laws require wastes identified as hazardous to be handled, stored, treated and disposed of according to the Missouri Hazardous Waste Management law. All non-exempt hazardous waste must be sent to an authorized facility.
There are three main ways pharmaceutical waste can be identified as a hazardous waste:
Pharmaceuticals that exhibit characteristics of hazardous wastes may contain arsenic, barium, cadmium, chloroform, chromium, lindane, selenium, silver, mercury or m-cresol. Mercury is used as a preservative in some vaccines and in phenyl mercuric acetate. M-cresol is used as a preservative in some insulin and vaccines. In addition, ignitable pharmaceuticals, or solutions containing more than 24% alcohol (such as compounding chemicals) or chemicals that are highly corrosive, can be hazardous waste.
If you are unsure if a pharmaceutical waste is a hazardous waste, contact the manufacturer. The manufacturer will be able to tell you the active ingredients in the pharmaceutical. The manufacturer should also be able to provide a Safety Data Sheet, which explains the potential hazards of the chemicals used in a product. It may also be necessary to analyze the pharmaceutical waste to determine if it is hazardous. More guidance about determining if waste is hazardous can be found through the Environmental Protection Agency’s website.
P-listed hazardous wastes include acutely hazardous commercial chemical products that have been or intend to be discarded. P-listed hazardous wastes have extremely hazardous properties that make them harmful in very small quantities. U-listed hazardous wastes include commercial chemical products that have been or intend to be discarded.
In order to qualify as a U- or P-listed hazardous waste, the waste must meet these two criteria:
The active chemical ingredients listed in paragraphs (e) and (f) of 40 C.F.R. § 261.33 are listed by chemical name, not necessarily by their common or commercial name. Most chemicals can be identified by more than one name. Cross-referencing chemical synonyms and verifying by Chemical Abstract Number must be done to confirm the chemical does not have another name on the P or U list. See the U.S. Environmental Protection Agency’s publication, Consolidated List of Chemicals Subject to EPCRA and Section 112(r) of the Clean Air Act, EPA550-B-01-003.
A list of common pharmaceutical precursors and ingredients that are U- or P-listed hazardous wastes is given in the following tables:
| Waste Code | Substance |
|---|---|
| P001 | Warfarin >0.3% |
| P012 | Arsenic trioxide |
| P042 | Epinephrine (not epinephrine salts) |
| P046 | Phentermine (not phentermine salts) |
| P075 | Nicotine and Salts |
| P188 | Physostigmine salicylate |
| P204 | Physostigmine |
Note: Medicinal nitroglycerin is not considered a P081 listed hazardous waste because it is not reactive.
| Waste Code | Substance |
|---|---|
| U010 | Mitomycin C |
| U034 | Chloral Hydrate |
| U035 | Chlorambucil |
| U044 | Chloroform |
| U058 | Cyclophosphamide |
| U059 | Daunomycin |
| U075 | Dichlorodifluromethane |
| U089 | Diethylstilbestrol |
| U117 | Ethyl Ether |
| U121 | Trichloromonofluromethane |
| U122 | Formaldehyde |
| U129 | Lindane (also can fail for toxicity) |
| U132 | Hexachlorophene |
| U141 | Isosafrole |
| U150 | Melphalan |
| U182 | Paraldehyde |
| U187 | Phenacetin |
| U188 | Phenol |
| U200 | Reserpine |
| U201 | Resorcinol |
| U203 | Safrole |
| U205 | Selenium Sulfide |
| U206 | Streptozotocin |
| U220 | Toluene |
Healthcare facilities, as defined in 40 C.F.R. § 266.500, operating and notifying under the requirements of Subpart P must use code “PHRM” or “PHRMS” in box 13 of the Uniform Hazardous Waste Manifest. Healthcare facilities may elect to include applicable waste codes alongside these codes.
According to 40 C.F.R. § 261.7(b)(3), a container or inner liner removed from a container that held an acute hazardous waste is empty if one of the three following procedures is followed:
According to 40 C.F.R. § 261.7(b)(1), a container or inner liner removed from a container that held a non-acute hazardous waste is empty if all wastes have been removed that can be removed using “commonly employed practices” for that type of container and one of the three following criteria are met:
RCRA-empty standards were modified for certain container types common to the healthcare industry. These changes are described at 40 C.F.R. § 266.507.
Aerosol inhalers could be considered delivery devices and other containers, as defined in 40 C.F.R. § 266.507(d). Healthcare facilities that generate these types of wastes, which remain unused, partially administered, or fully administered, must manage them as non-creditable hazardous waste pharmaceuticals unless the container held a non-acute hazardous waste and is empty as defined in 40 C.F.R. § 261.7(b)(1) or (2).
Intravenous (IV) bags that contain hazardous waste pharmaceuticals are considered empty when the bag has been fully administered to a patient, or if the IV bag held a non-acute hazardous waste pharmaceuticals and is empty as defined in 40 C.F.R. § 261.7(b)(1). Applicable infectious waste regulations still apply.
Syringes are considered empty when the contents have been removed by fully depressing the plunger of the syringe. If the syringe is not empty it must be managed as a non-creditable hazardous waste pharmaceutical. Applicable infectious waste regulations still apply.
A stock bottle, dispensing bottle, vial, ampule or unit-dose container that does not exceed 1 liter or 10,000 pills is considered empty provided that the pharmaceuticals have been removed from the container using the practices commonly employed to remove materials from those types of containers.
Nothing in this document may be used to implement any enforcement action or levy any penalty unless promulgated by rule under chapter 536 or authorized by statute.
Division of Environmental Quality
P.O. Box 176
Jefferson City, MO 65102-0176
United States
Division of Environmental Quality
P.O. Box 176
Jefferson City, MO 65102-0176
United States