URANIUM-238
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
IDENTIFIERS
USES/FORMS/SOURCES
Commercial uses of uranium include nuclear power reactors and nuclear weapons, armor-piercing ammunition, inertial guidance systems and gyro compasses, radiation shielding, and x-ray targets (Budavari, 1996).
URANIUM-238 (U-238) is a dense, ductile, malleable, lustrous, radioactive metal of the actinide series (Budavari, 1996; Lewis, 1993). Pure uranium is not an external radiation hazard, as it emits mainly low energy alpha-radiation of 4.2 Mev. U-238 has a half-life of 4.5 x 10(9) years. It decays to the stable isotope of Pb-206 (LEAD). There are some beta- and gamma-emissions from uranium ore. Uranium is highly reactive and never occurs in the metallic form in nature (Clayton & Clayton, 1994). It can occur in the +3, +4, +5 or +6 valence states, with +6 being the most stable (ACGIH, 1992). Most +4 compounds are oxidized to the +6 state during biological absorption (ACGIH, 1992). Metallic uranium reacts with nearly all non-metals and is attacked by water, acids and peroxides (Budavari, 1996; Lewis, 1993). The powdered metal is a dangerous fire risk and ignites spontaneously in air (Lewis, 1993). Important soluble uranium compounds are the nitrate, fluoride, and hexafluoride, while insoluble ones include the dioxide and tetrafluoride (Hathaway et al, 1991).
The principle substances for occupational and environmental exposure to uranium-238 are RADIUM-226, RADON-222, and the short-lived RADON DAUGHTERS (Colle R, 1980). The dose to the lungs from inhalation of radon is mainly due to alpha-emissions from radon-222 and radon daughters, and not to radon itself (Colle R, 1980). Exposure to radon and its daughters in stone or brick dwellings may play an important role in the etiology of lung cancer in the general population (Edling, 1984), as half of the total background exposure to ionizing radiation is thought to be from radon daughters. Other non-occupational exposures to uranium include peat bogs, coal power plants, mining and milling wastes, and dietary intake. Some exposure can occur from leaching of uranium pigments used in pottery and stoneware by acidic foods. Daily dietary intake of uranium is approximately 1.75 mcg in the normal US diet, and the total body burden in non-occupationally exposed persons has been estimated at 100 to 125 mcg (ACGIH, 1992; Clayton & Clayton, 1994). Occupational exposure to uranium occurs during uranium mining, although silicosis may be a greater risk for miners (EOSH, 1982). Occupational exposures are mainly by inhalation. Critical organs are the KIDNEYS and the LUNGS (EOSH, 1982).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Editor's Note: An ERG guide with information appropriate to this material does not exist.
ACUTE CLINICAL EFFECTS
- The radiation hazard of uranium is greater than its chemical hazard (Clayton & Clayton, 1994). Aside from the radiation hazard, the soluble uranium compounds are more toxic than the insoluble ones (Hathaway et al, 1991).
- Although U-238 is not an external radiation hazard, it is a highly toxic element on an acute basis if it enters the body. The soluble compounds are a hazard to the liver and kidneys, especially the renal tubules (ILO, 1983; Hathaway et al, 1991). The high toxicity of insoluble uranium compounds is largely due to irradiation of the lung from inhaled particles.
- Uranium and its salts are highly toxic chemicals. Dermatitis, possible basaloma (Sevcova, 1976), acute necrotic arterial lesions, and sudden death may occur (Donoghue, 1972).
- Acute renal failure, refractory anemia, rhabdomyolysis, myocarditis, liver dysfunction, coagulopathy and paralytic ileus occurred in a case of deliberate ingestion of 15 grams of uranium acetate. Renal impairment was still present 6 months later (Pavlakis et al, 1996).
- Insoluble uranium compounds mostly remain in the lung after inhalation (Hathaway et al, 1991).
- Acute exposure to high levels of ionizing radiation produces RADIATION SICKNESS, also known as ACUTE RADIATION SYNDROME. This condition occurs generally with acute exposure to greater than 100 RADs, and has four distinct phases: prodrome, latent, manifest illness, and recovery.
- Other effects of acute exposure to ionizing radiation are erythema and burns of the skin.
CHRONIC CLINICAL EFFECTS
- Uranium metal and insoluble compounds can cause dermatitis (Budavari, 1996).
- A study of uranium miners showed an increased incidence of abnormal sputum cytology, much greater in smokers than nonsmokers (Band, 1982). Other toxic effects of uranium include renal aminoaciduria, renal tubular necrosis (Black, 1965), pulmonary abnormalities, dyspnea (Samet, 1984), and pneumoconiosis (Cooper, 1968).
- There is a possible connection between radon daughters attached to dust particles in uranium mines and enhancement of the pulmonary fibrogenic effect of silica (Trapp, 1970).
- Studies in hamsters demonstrated that exposure to uranium dust causes inflammation and proliferative pulmonary changes, as well as carcinomas, with high-level exposure to radon daughters (Cross, 1981). Experimental animal studies have reported the effects of both acute (subcutaneous injection) and chronic (oral) uranium poisoning on autoimmune processes in the thyroid (Malenchenko, 1978) and on the TESTES (Malenchenko & Barkun, 1976).
- A Czech study showed a significant and continuous decrease in cholinesterase activity in uranium miners, related to duration of exposure (Pehr & Nosek, 1973).
- Pb-210 and Po-219 (as U-238 decay products) have been found in the soft tissues and skeletons of uranium miners, indicating a systemic distribution of uranium (Blanchard & Moore, 1971). Uranium mining is also associated with tuberculosis and other non-malignant respiratory diseases, but the data do not allow any firm conclusions as to the possible role of uranium (Waxweiler, 1983). The pattern is suggestive of an immunosuppressive effect.
- There is a possible radiation effect of uranium on hematopoiesis in the bone marrow (Vich, 1970). A study in uranium miners found that immune suppression accompanied development of lung cancer (p 4).
-RANGE OF TOXICITY
MAXIMUM TOLERATED EXPOSURE
- Carcinogenicity Ratings for CAS7440-61-1 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A1 ; Listed as: Uranium (natural) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): A1 ; Listed as: Uranium (natural), soluble and insoluble compounds, as U EPA (U.S. Environmental Protection Agency, 2011): Information reviewed but value not estimated. Refer to Full IRIS Summary. ; Listed as: Uranium, natural IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): Not Listed NIOSH (National Institute for Occupational Safety and Health, 2007): Ca ; Listed as: Uranium (insoluble compounds, as U) NIOSH (National Institute for Occupational Safety and Health, 2007): Ca ; Listed as: Uranium (soluble compounds, as U) MAK (DFG, 2002): Not Listed NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed
TOXICITY AND RISK ASSESSMENT VALUES
- EPA Risk Assessment Values for CAS7440-61-1 (U.S. Environmental Protection Agency, 2011):
Oral: Inhalation: Drinking Water:
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS7440-61-1 (American Conference of Governmental Industrial Hygienists, 2010):
Editor's Note: The listed values are recommendations or guidelines developed by ACGIH(R) to assist in the control of health hazards. They should only be used, interpreted and applied by individuals trained in industrial hygiene. Before applying these values, it is imperative to read the introduction to each section in the current TLVs(R) and BEI(R) Book and become familiar with the constraints and limitations to their use. Always consult the Documentation of the TLVs(R) and BEIs(R) before applying these recommendations and guidelines. Adopted Value Adopted Value
- AIHA WEEL Values for CAS7440-61-1 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS7440-61-1 (National Institute for Occupational Safety and Health, 2007):
Listed as: Uranium (insoluble compounds, as U) REL: Listed as: Uranium (soluble compounds, as U) REL: IDLH: IDLH: 10 mg Uranium/m3 Note(s): Ca
IDLH: IDLH: 10 mg Uranium/m3 Note(s): Ca
- OSHA PEL Values for CAS7440-61-1 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
Listed as: Uranium (as U) - Soluble compounds Table Z-1 for Uranium (as U) - Soluble compounds: 8-hour TWA: ppm: mg/m3: 0.05 Ceiling Value: Skin Designation: No Notation(s): Not Listed
Listed as: Uranium (as U) - Insoluble compounds Table Z-1 for Uranium (as U) - Insoluble compounds: 8-hour TWA: ppm: mg/m3: 0.25 Ceiling Value: Skin Designation: No Notation(s): Not Listed
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS7440-61-1 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS7440-61-1 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS7440-61-1 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS7440-61-1 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS7440-61-1 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS7440-61-1 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS7440-61-1 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS7440-61-1 (EPA, 2005):
LABELS
- NFPA Hazard Ratings for CAS7440-61-1 (NFPA, 2002):
-PERSONAL PROTECTION
SUMMARY
- Editor's Note: An ERG guide with information appropriate to this material does not exist.
PROTECTIVE CLOTHING
- CHEMICAL PROTECTIVE CLOTHING. Search results for CAS 7440-61-1.
-PHYSICAL HAZARDS
FIRE HAZARD
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS7440-61-1 (NFPA, 2002):
- FIRE CONTROL/EXTINGUISHING AGENTS
- Editor's Note: An ERG guide with information appropriate to this material does not exist.
- NFPA Extinguishing Methods for CAS7440-61-1 (NFPA, 2002):
EVACUATION PROCEDURES
- Editor's Note: An ERG guide with information appropriate to this material does not exist.
- AIHA ERPG Values for CAS7440-61-1 (AIHA, 2006):
- DOE TEEL Values for CAS7440-61-1 (U.S. Department of Energy, Office of Emergency Management, 2010):
Listed as Uranium TEEL-0 (units = mg/m3): 0.25 TEEL-1 (units = mg/m3): 0.6 TEEL-2 (units = mg/m3): 2.5 TEEL-3 (units = mg/m3): 10 Definitions: TEEL-0: The threshold concentration below which most people will experience no adverse health effects. TEEL-1: The airborne concentration (expressed as ppm [parts per million] or mg/m(3) [milligrams per cubic meter]) of a substance above which it is predicted that the general population, including susceptible individuals, could experience notable discomfort, irritation, or certain asymptomatic, nonsensory effects. However, these effects are not disabling and are transient and reversible upon cessation of exposure. TEEL-2: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience irreversible or other serious, long-lasting, adverse health effects or an impaired ability to escape. TEEL-3: The airborne concentration (expressed as ppm or mg/m(3)) of a substance above which it is predicted that the general population, including susceptible individuals, could experience life-threatening adverse health effects or death.
- AEGL Values for CAS7440-61-1 (National Research Council, 2010; National Research Council, 2009; National Research Council, 2008; National Research Council, 2007; NRC, 2001; NRC, 2002; NRC, 2003; NRC, 2004; NRC, 2004; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2005; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2007; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2006; 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National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2009; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances, 2008; 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62 FR 58840, 1997; 65 FR 14186, 2000; 65 FR 39264, 2000; 65 FR 77866, 2000; 66 FR 21940, 2001; 67 FR 7164, 2002; 68 FR 42710, 2003; 69 FR 54144, 2004):
- NIOSH IDLH Values for CAS7440-61-1 (National Institute for Occupational Safety and Health, 2007):
IDLH: 10 mg Uranium/m3 Note(s): Ca IDLH: 10 mg Uranium/m3 Note(s): Ca
CONTAINMENT/WASTE TREATMENT OPTIONS
-PHYSICAL/CHEMICAL PROPERTIES
-REFERENCES
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- 65 FR 77866: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2000.
- 66 FR 21940: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2001.
- 67 FR 7164: Notice of the National Advisory Committee for Acute Exposure Guideline Levels for Hazardous Substances - Proposed AEGL Values, Environmental Protection Agency, NAC/AEGL Committee. National Archives and Records Administration (NARA) and the Government Publishing Office (GPO), Washington, DC, 2002.
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