THORIUM-230
HAZARDTEXT ®
Information to help in the initial response for evaluating chemical incidents
-IDENTIFICATION
SYNONYMS
IDENTIFIERS
USES/FORMS/SOURCES
Thorium is used in alloys, ceramics, lighting mantles, nuclear fuels and nuclear research (Clayton & Clayton, 1994).
THORIUM-230 (Th-230) is a radioactive isotope of THORIUM . Its half-life is 7.6 x 10(4) years. Th-230 decays by emitting alpha-particles of 4.6 MeV with some beta- and gamma- emissions to form RADIUM-226. As a decay daughter of URANIUM-238, Th-230 is part of the uranium/radium 4n + 2 decay series. Thorium is a radioactive metal of the actinide series (Lewis, 1993; Clayton & Clayton, 1994). It is a soft, bright metal with a silvery luster when freshly cut (Lewis, 1993). Thorium in general is chemically similar to uranium, and exists as hydrides, dioxide, fluoride, sulfate, nitrate, oxalate, and also forms complex salts (EOHS, 1982). The principle toxicological hazard of thorium, however, is from ionizing radiation and its ultimate decay products, RADON-222 and RADON DAUGHTERS (p 131). Th-230 together with radium-226 are the most hazardous components of uranium tailings (p 8) because of their long half-lives. The ultimate fate of thorium in the body is somewhat determined by its physical form upon entry. It may be an inorganic salt, a chelate complex with iron, or a colloidal suspension, as in the case of Thorotrast, the former radiocontrast agent. Thorotrast itself was of varying composition (Clayton & Clayton, 1994).
While occupational exposures occur mainly in uranium mining and in processing of thorium for metallurgical and nuclear uses (EOHS, 1982), some nonoccupational exposure can occur from aquatic, terrestrial, and airborne sources. A potential exposure pathway for all thorium isotopes in children is ingestion of raw monazite sand (p 5). Some contribution to the natural thorium exposure is thought to occur from combustion of fossil fuels (Harley & Pasternack, 1979).
-CLINICAL EFFECTS
GENERAL CLINICAL EFFECTS
- Editor's Note: An ERG guide with information appropriate to this material does not exist.
ACUTE CLINICAL EFFECTS
- Acute exposure to high levels of ionizing radiation produces RADIATION SICKNESS, also known as ACUTE RADIATION SYNDROME. This condition generally occurs 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.
- Most of the data on health risks of thorium come from studies of persons who received Thorotrast contrast medium for radiography. An estimated 50,000 people were exposed to thorium dioxide in Thorotrast worldwide between 1929 and the mid 1950's (Kesava et al, 1996). After 33 cases of cancer of the liver, larynx, and bronchi, and sarcoma of the kidneys were found in this population, the use of Thorotrast was discontinued (ILO, 1983). Even acute thorium exposure can subsequently lead to cancer.
- Intense chronic granulomas, called "thorotrastomas," can develop at sites of extravasation of the contrast agent at the site of arterial puncture. These often arise in the neck from the carotid artery after carotid arteriography. The fibrotic response may involve much of the neck and affect the lower cranial nerves (IX through XII) to produce neuropathies (Kesava et al, 1996).
- Other reported effects include nonspecific compressive symptoms (e.g., dyspnea and dysphagia), vascular occulsion and rupture, and severe oropharyngeal hemorrhage due to pseudoaneurysm (Kesava et al, 1996).
CHRONIC CLINICAL EFFECTS
- Thorium has a very long retention time; measurement of body burdens of Th-230 are thought to give an estimate of lifelong cumulative exposure (pp 799-1980). Important considerations for the toxicity of Th-230 are its long half-life and long biological retention time, which both would cause thorium to have CUMULATIVE TOXICITY. The major routes of uptake of Th-230 are inhalation and ingestion (p 131).
- The concentration of Th-230 decreases in the following order in human tissues in persons not occupationally exposed: lymph nodes > lung > bone > kidney > liver. Th-230 has approximately the same body distribution as Th-232, with about 11-27% in the lung and 55-70% in the skeleton. Th-230 concentration in the bone increases linearly with age (Wrenn et al, 1982; (pp 799-1980).
- Chronic exposure to dust localizes the thorium in the interstitial spaces and alveolar bronchial membranes of the lungs (Pavlovskaya, 1976). In a study of Colorado miners, the lungs contained 65 times higher concentrations of Th-230 at autopsy than those of non-miners (pp 799-1980). The actual distribution of Th-230 in the body of a given individual would depend somewhat on the particular thorium compounds to which he or she had been exposed, as some are insoluble and some are relatively soluble (EOHS, 1982). Th-230 is preferentially retained in the body over U-234 and U-238 (Fisher, 1983).
-RANGE OF TOXICITY
MAXIMUM TOLERATED EXPOSURE
- Carcinogenicity Ratings for CAS14269-63-7 :
ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed EPA (U.S. Environmental Protection Agency, 2011): Not Listed 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): Not Listed 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 CAS14269-63-7 (U.S. Environmental Protection Agency, 2011):
-STANDARDS AND LABELS
WORKPLACE STANDARDS
- ACGIH TLV Values for CAS14269-63-7 (American Conference of Governmental Industrial Hygienists, 2010):
- AIHA WEEL Values for CAS14269-63-7 (AIHA, 2006):
- NIOSH REL and IDLH Values for CAS14269-63-7 (National Institute for Occupational Safety and Health, 2007):
- OSHA PEL Values for CAS14269-63-7 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
- OSHA List of Highly Hazardous Chemicals, Toxics, and Reactives for CAS14269-63-7 (U.S. Occupational Safety and Health Administration, 2010):
ENVIRONMENTAL STANDARDS
- EPA CERCLA, Hazardous Substances and Reportable Quantities for CAS14269-63-7 (U.S. Environmental Protection Agency, 2010):
- EPA CERCLA, Hazardous Substances and Reportable Quantities, Radionuclides for CAS14269-63-7 (U.S. Environmental Protection Agency, 2010):
- EPA RCRA Hazardous Waste Number for CAS14269-63-7 (U.S. Environmental Protection Agency, 2010b):
- EPA SARA Title III, Extremely Hazardous Substance List for CAS14269-63-7 (U.S. Environmental Protection Agency, 2010):
- EPA SARA Title III, Community Right-to-Know for CAS14269-63-7 (40 CFR 372.65, 2006; 40 CFR 372.28, 2006):
- DOT List of Marine Pollutants for CAS14269-63-7 (49 CFR 172.101 - App. B, 2005):
- EPA TSCA Inventory for CAS14269-63-7 (EPA, 2005):
LABELS
- NFPA Hazard Ratings for CAS14269-63-7 (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 14269-63-7.
-PHYSICAL HAZARDS
FIRE HAZARD
- FLAMMABILITY CLASSIFICATION
- NFPA Flammability Rating for CAS14269-63-7 (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 CAS14269-63-7 (NFPA, 2002):
EVACUATION PROCEDURES
- Editor's Note: An ERG guide with information appropriate to this material does not exist.
- AIHA ERPG Values for CAS14269-63-7 (AIHA, 2006):
- DOE TEEL Values for CAS14269-63-7 (U.S. Department of Energy, Office of Emergency Management, 2010):
- AEGL Values for CAS14269-63-7 (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, 2008; 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, 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; 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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 CAS14269-63-7 (National Institute for Occupational Safety and Health, 2007):
CONTAINMENT/WASTE TREATMENT OPTIONS
-PHYSICAL/CHEMICAL PROPERTIES
-REFERENCES
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