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By Willard R. Chappel, Charles O. Abernathy and Rebecca L. Calderon (Eds.)

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Extra resources for Arsenic Exposure and Health Effects III. Proceedings of the Third International Conference on Arsenic Exposure and Health Effects, July 12–15, 1998, San Diego, California

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Sister-chromatid exchange (See) among individuals chronically exposed to arsenic in drinking water. , 312 (2), 111-120. -L. 1998. Arsenic species in drinking water, hair, fingernails, and urine of patients with blackfoot disease. /. Toxicol Environ. Health, 53,85-93. C and Chakraborti, D. 1996. Arseiuc in grotmdwater in seven districts of West Bengal, India—The biggest arsenic calamity in the world. Curr. Sci, 70 (11), 976-986. , Roels, H. and Lauwerys, R. 1981. The metabolism of arseruc in humans acutely intoxicated by AS2O3 Its significance for the duration of the BAL therapy.

Environ. Health, 48,111-118. , Lauwerys, R. and Fagard, R. 1996. Geographical and temporal differences in the luinary excretion of inorganic arsenic: a Belgian population study. Occup. Environ. , 53,320-327. K. C. 1998. Calcutta's industrial pollution: groundwater arsenic contamination in a residential area and sufferings of people due to industrial effluent discharge—an eight-year study report. Current Science, 74 (4), 346-355. , Samanta, G. and Chakraborti, D. 1995. Arsenic in ground water in six districts of West Bengal, India: the biggest arsenic calamity in the world.

Analytic results from this laboratory compared favorably with other laboratories partidpating in an inter-laboratory comparison study (Crecelius and Yager, 1997). Arsenic Lung Deposition To estimate the amount of arsenic deposited, each stage of the impactor was treated as a monodisperse aerosol with a mass median aerodynamic diameter (MMAD) equal to the stated cut size. S. S. EPA, 1994), which is based on the work of Menache et al. (1995), was used to estimate the mass of arsenic deposited in each region of the respiratory tract for the aerosol MMAD representing each impactor stage.

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