Inhalation toxicity sulfur mustard

The data base for sulfur mustard contains two developmental toxicity studies in different species, a reproductive bioassay and a standard subchronic toxicity study in one species. In addition, chronic inhalation studies have been conducted on sulfur mustard using rats, mice, guinea pigs and dogs. The principal study identifies a toxic effect that is consistent with the vesicant properties of sulfur mustard. There is no evidence that any other experimental species would be more sensitive to ingested sulfur mustard therefore, additional oral toxicity studies in other species are not considered critical. 

U.S. EPA (1991) derived a cancer inhalation unit risk for sulfur mustard based on the results of inhalation animal studies conducted by McNamara et al. (1975, see Section 3.7.2) however, it was emphasized in the EPA report that the studies of McNamara et al. (1975) contained deficiencies which made a quantitative analysis difficult. Conducted in 1970, the studies do not conform to the modem norms of acceptable experimental protocol, and it is likely that there was bias in the assignment of the animals to the test categories (U.S. EPA, 1991). In addition, many of the exposures were very brief, included only a few animals, and many of the animals were sacrificed (and some were replaced) before their capacity to develop late-appearing tumors was fully developed (U.S. EPA, 1991). Despite these shortcomings, it was noted by EPA that the McNamara et al. data are the best available for estimating the carcinogenic potency of sulfur mustard. The authors of the EPA report analyzed two sets of McNamara s data one from a toxicity study and one from a carcinogenicity study (see Section 3.7.2). 

War I. More recent use occurred in Middle East conflicts. Its oily nature makes it persistent on surfaces it contacts. Because sulfur mustard exerts toxic effects following dermal, ocular, and inhalation exposure, its use necessitated fiill body protection which, in tmn, required the development of protective clothing and significant changes in warfare operations. 

Ocular, percutaneous, inhalation, ingestion, and injection are all possible routes of exposure. Effects may be local, systemic, or both. All of the nitrogen mustards are oily liquids that are colorless to pale yellow and evaporate slowly. They are more dangerous than sulfur mustard but, like sulfur mustard, they are derivatives of ammonia. The most toxic and most volatile of the three nitrogen mustards is HN-2, but HN-3 is used more because it is stable. 

Anderson, D.R., Yourick, J.J., Moeller, R.B., et al., 1996. Pathologic changes in rat lungs following acute sulfur mustard inhalation. Inhal. Toxicol. 8, 285-297. Anzueto, A., Delemos, R.A., Seidenfeld, J., et al., 1990. Acute inhalation toxicity of soman and sarin in baboons. Fund. Appl. Toxicol. 14, 676-687. 

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