INTERNATIONAL PROGRAMME ON CHEMICAL SAFETY WORLD HEALTH ORGANIZATION SUMMARY OF TOXICOLOGICAL DATA OF CERTAIN FOOD ADDITIVES AND CONTAMINANTS WHO FOOD ADDITIVES SERIES NO. 13 The data contained in this document were examined by the Joint FAO/WHO Expert Committee on Food Additives* Rome, 3-12 April 1978 Food and Agriculture Organization of the United Nations World Health Organization * Twenty-second Report of the Joint FAO/WHO Expert Committee on Food Additives, Geneva, 1978, WHO Technical Report Series No. 631 ASBESTOS Explanation Asbestos was evaluated by the Joint FAO/WHO Expert Committee on Food Additives in 1974. Additional data have become available since the last evaluation and are summarized below. BIOLOGICAL DATA Long-term studies Rat In two studies containing 10 and 40 animals/group respectively, male rats were fed 0 and 1% chrysotite asbestos for their lifetime. In the first study, six malignant tumours were found in the treated animals compared to one malignant tumour in the controls. In the second study, 11 malignant tumours were observed in each group. Two of the tumours in the treated animals were associated with the gastrointestinal tract. A third study was performed in which two groups of 10 male rats were fed 0 end 1% asbestos for six weeks. At the time of sacrifice tissues were analysed for asbestos fibres. All tissues of the treated animals showed higher levels of fibres than the controls. The highest level was found in the omentum (Cunningham et al., 1978). Epidemiology Twenty-two municipalities in Quebec, grouped by evidence of exposure to asbestos fibres in their municipal water supplies (known high, probable high and probable low exposures), were evaluated in respect to mortality experience. The expected number of cancer deaths were calculated by applying the Quebec age-specific (five-year groups), sex-specific, site-specific and period-specific (1965-1967, 1970-1972) mortality rates to the 1966 or 1971 census populations for each municipality. Excess mortality due to cancer of the stomach and lungs in males, and pancreas in females, was observed in the two asbestos mining municipalities with known high exposures. The excess mortality among males was probably due to occupational exposure to asbestos. The absence of excess mortality due to pancreatic cancer in the male would suggest that the excess among females was not due to waterborne asbestos. The author concluded that the evidence derived from this study would indicate that the excess mortality due to cancer could not be attributed to exposure to asbestos in the drinking-water (Wigle, 1977). REFERENCES Cunningham, H. M., Moodie, C. A., Lawrence, G. A. and Pontefract, R. D. (1978) Chronic effects of ingested asbestos in rats, Arch. Environ. Contamination and Toxicol. (In press) International Agency for Research on Cancer (1973) IARC Monographs on the evaluation of carcinogenic risk of chemicals to man. Some inorganic and organometallic compounds, vol. 2, p. 17, Lyon, IARC International Agency for Research on Cancer (1977) IARC Monographs on the evaluation of carcinogenic risk of chemicals to man. Asbestos, Vol. 14, Lyon, IARC Wigle, M.D. (1977) Cancer mortality in relation to asbestos in municipal water supplies, Arch. environm. Hlth, 32, 185
See Also: Toxicological Abbreviations ASBESTOS (JECFA Evaluation) Asbestos (IARC Summary & Evaluation, Supplement7, 1987) Asbestos (IARC Summary & Evaluation, Volume 2, 1973) Asbestos (IARC Summary & Evaluation, Volume 14, 1977)