lewisite and cyanogen-chloride

Health risk assessments for sites contaminated with chemical warfare agents require a comparison of the potential levels of exposure with a characterization of the toxic potency of each chemical. For noncancer health effects, toxic potency is expressed in terms of Reference Doses (RfD). A RfD is a daily exposure level or dose (usually expressed in units of milligrams of chemical per kilogram body weight per day) for the human population, including sensitive subpopulations, that is likely to be without an appreciable risk of deleterious effects. A daily exposure at or below the RfD is not likely to be associated with health risks, but as the amount of chemical that an individual is exposed to increases above the RfD, the probability that an adverse effect will occur also increases. A RfD is derived by first examining the available human or animal toxicity data to identify a dose or exposure that corresponds to a no-observed-adverse-effect level (NOAEL) or a lowest-observed-adverse-effect level (LOAEL). The NOAEL is the exposure level at which there are no statistically or biologically significant increases in frequency or severity of adverse effects between the exposed population and its appropriate control. Effects may be produced at this level, but they are not considered to be adverse if they do not result in functional impairment or pathological lesions that affect the performance of the whole organism or which reduce an organism's ability to cope with additional challenge. The LOAEL is the lowest exposure level at which there are statistically or biologically significant increases in frequency or severity of adverse effects between the exposed population and its appropriate control. If only a LOAEL is identified by the toxicity data, a NOAEL is estimated by dividing the LOAEL by a factor no greater than 10. This extrapolation factor of 10 or less is termed the LOAEL-to-NOAEL Uncertainty Factor (UFL). The NOAEL is also adjusted by the application of other Uncertainty Factors, including (1) a UFH < or = 10 to ensure that the resulting RfD protects segments of the human population that may be more sensitive to the chemical than the average person; (2) a UFA < or = 10 to extrapolate from the experimental animal species to humans; (3) a UFS < or = 10 to extrapolate from an experimental subchronic exposure study to a potential chronic exposure; and (4) a UFD < or = 10 to ensure that the resulting RfD is protective for all possible adverse effects, particula

Topics: Air Pollutants; Animals; Arsenic Poisoning; Arsenicals; Chemical Warfare Agents; Cholinesterase Inhibitors; Cyanides; Environmental Monitoring; Hazardous Waste; Humans; Mechlorethamine; Mustard Compounds; Mustard Gas; No-Observed-Adverse-Effect Level; Rats; Reference Values; Risk Assessment; United States