Technology Transfer Network - Air Toxics Web Site
Methyl Iodide (Iodomethane)
Hazard Summary-Created in April 1992; Revised in January 2000
Methyl iodide is used as an intermediate in the manufacture of some pharmaceuticals
and pesticides, in methylation processes, and in the field of microscopy.
In humans, acute (short-term) exposure to methyl iodide by inhalation
may depress the central nervous system (CNS), irritate the lungs and skin,
and affect the kidneys. Massive acute inhalation exposure to methyl
iodide has led to pulmonary edema. Acute inhalation exposure of
humans to methyl iodide has resulted in nausea, vomiting, vertigo, ataxia,
slurred speech, drowsiness, skin blistering, and eye irritation.
Chronic (long-term) exposure of humans to methyl iodide by inhalation
may affect the CNS and cause skin burns. EPA has not classified
methyl iodide for potential carcinogenicity.
- Methyl iodide is used as an intermediate in the manufacture of some pharmaceuticals and pesticides. It is also used in methylation processes and in the field of microscopy. (1,2,4)
- Proposed uses of methyl iodide are as a fire extinguisher and as an insecticidal fumigant. (5)
Sources and Potential Exposure
- Individuals are most likely to be exposed to methyl iodide in the workplace. (1)
- Methyl iodide occurs naturally in the ocean as a product of marine algae. (2)
Assessing Personal Exposure
- No information was located regarding the measurement of personal exposure to methyl iodide.
Health Hazard InformationAcute Effects:
- Massive acute inhalation exposure to methyl iodide has led to pulmonary edema. Depression of the CNS, irritation of the lungs and skin, and effects on the kidneys may result in acutely exposed humans. (3-5)
- Acute inhalation exposure of humans to methyl iodide has resulted in nausea, vomiting, vertigo, ataxia, slurred speech, drowsiness, skin blistering, and eye irritation. (2,3,5,6)
- Tests involving acute exposure of rats and mice have shown methyl iodide to have moderate to high acute toxicity by inhalation, and high acute toxicity by ingestion. (6)
- Chronic inhalation exposure to methyl iodide may affect the CNS in humans. (4)
- Prolonged dermal contact with methyl iodide may cause skin burns in humans and animals. (1,4)
- EPA has not established a Reference Concentration (RfC) or a Reference Dose (RfD) for methyl iodide.
- No information is available on the reproductive or developmental effects of methyl iodide in humans or animals.
- No information is available on the carcinogenic effects of methyl iodide in humans.
- There is limited evidence that methyl iodide is carcinogenic in animals, with lung tumors observed in studies of mice and rats. In rats that received subcutaneous injections, subcutaneous sarcomas and pulmonary metastases were reported. An increased incidence of lung tumors was reported in mice exposed to high levels of methyl iodide by intraperitoneal injection. (2,3)
- EPA has not classified methyl iodide for potential carcinogenicity.
- The chemical formula for methyl iodide is CH3I, and its molecular weight is 141.95 g/mol. (2,4)
- Methyl iodide occurs as a colorless nonflammable liquid that turns brown on exposure to light and is slightly soluble in water. (2,4)
- Methyl iodide has a pungent odor, but its odor threshold has not been established. (2)
- The vapor pressure for methyl iodide is 400 mm Hg at 25 °C, and its log octanol/water partition coefficient (log Kow) is 1.51. (2,3)
To convert concentrations in air (at 25 °C) from ppm to mg/m3: mg/m3 = (ppm) × (molecular weight of the compound)/(24.45). For methyl iodide: 1 ppm = 5.81 mg/m3. To convert concentrations in air from µg/m3 to mg/m3: mg/m3 = (µg/m3) × (1 mg/1,000 µg).
Health Data from Inhalation Exposure
ACGIH TLV--American Conference of Governmental and Industrial
Hygienists' threshold limit value expressed as a time-weighted average;
the concentration of a substance to which most workers can be exposed
without adverse effects.
AIHA ERPG--American Industrial Hygiene Association's emergency response planning guidelines. ERPG 1 is the maximum airborne concentration below which it is believed nearly all individuals could be exposed up to one hour without experiencing other than mild transient adverse health effects or perceiving a clearly defined objectionable odor; ERPG 2 is the maximum airborne concentration below which it is believed nearly all individuals could be exposed up to one hour without experiencing or developing irreversible or other serious health effects that could impair their abilities to take protective action.
LC50 (Lethal Concentration50)--A calculated concentration of a chemical in air to which exposure for a specific length of time is expected to cause death in 50% of a defined experimental animal population.
NIOSH REL--National Institute of Occupational Safety and Health recommended exposure limit; NIOSH-recommended exposure limit for an 8- or 10-h time-weighted-average exposure and/or ceiling.
NIOSH IDLH-- NIOSH's immediately dangerous to life or health concentration; NIOSH recommended exposure limit to ensure that a worker can escape from an exposure condition that is likely to cause death or immediate or delayed permanent adverse health effects or prevent escape from the environment.
OSHA PEL--Occupational Safety and Health Administration's permissible exposure limit expressed as a time-weighted average; the concentration of a substance to which most workers can be exposed without adverse effect averaged over a normal 8-h workday or a 40-h workweek.
The health and regulatory values cited in this factsheet were obtained
in December 1999.
a Health numbers are toxicological numbers from animal testing or risk assessment values developed by EPA.
b Regulatory numbers are values that have been incorporated in Government regulations, while advisory numbers are nonregulatory values provided by the Government or other groups as advice. OSHA numbers are regulatory, whereas NIOSH, ACGIH, and AIHA numbers are advisory.
- M. Sittig. Handbook of Toxic and Hazardous Chemicals and Carcinogens. 2nd ed. Noyes Publications, Park Ridge, NJ. 1985.
- International Agency for Research on Cancer (IARC). IARC Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Man. Some Fumigants, the Herbicides 2,4-D and 2,4,5-T, Chlorinated Dibenzodioxins and Miscellaneous Industrial Chemicals. Volume 15. World Health Organization, Lyon. 1977.
- U.S. Department of Health and Human Services. Hazardous Substances Data Bank (HSDB, online database). National Toxicology Information Program, National Library of Medicine, Bethesda, MD. 1993.
- The Merck Index. An Encyclopedia of Chemicals, Drugs, and Biologicals. 11th ed. Ed. S. Budavari. Merck and Co. Inc., Rahway, NJ. 1989.
- G.D. Clayton and F.E. Clayton, Eds. Patty's Industrial Hygiene and Toxicology. Volume IIB. 3rd revised ed. John Wiley & Sons, New York. 1981.
- U.S. Department of Health and Human Services. Registry of Toxic Effects of Chemical Substances (RTECS, online database). National Toxicology Information Program, National Library of Medicine, Bethesda, MD. 1993.
- National Institute for Occupational Safety and Health (NIOSH). Pocket Guide to Chemical Hazards. U.S. Department of Health and Human Services, Public Health Service, Centers for Disease Control and Prevention. Cincinnati, OH. 1997.
- American Industrial Hygiene Association (AIHA). The AIHA 1998 Emergency Response Planning Guidelines and Workplace Environmental Exposure Level Guides Handbook. 1998.
- Occupational Safety and Health Administration (OSHA). Occupational Safety and Health Standards, Toxic and Hazardous Substances. Code of Federal Regulations 29 CFR 1910.1000. 1998.
- American Conference of Governmental Industrial Hygienists (ACGIH). 1999 TLVs and BEIs. Threshold Limit Values for Chemical Substances and Physical Agents. Biological Exposure Indices. Cincinnati, OH. 1999.