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dose group; in addition, 3/12 animals exposed to the 5000 mg/kg diet for 10 weeks had thyroid tumors.<br />

Clitoral gland tumors (squamous-cell, sebaceous-cell or squamous-sebaceous-cell carcinomas) were<br />

noted in 0/37 controls, 8/47 of the low-dose group, 15/33 of the mid-dose group and 9/40 of the high<br />

dose-group, as well as in 1/12 of the animals in the 10 week high-dose group.<br />

IV.<br />

DERIVATION OF CANCER POTENCY<br />

Basis for Cancer Potency<br />

Cancer potency for 2, 4-diaminoanisole was derived from that for the sulfate using a molecular weight<br />

conversion (Cal/EPA, 1992):<br />

q h (base) = q h (sulfate) ×<br />

MW(sulfate)<br />

MW(base)<br />

where q h is the human potency and MW is the molecular weight. This conversion assumes that the<br />

intake of equivalent moles of the two forms of the chemical results in equivalent concentrations of the<br />

active species in vivo. Gold et al. (1984) list the results of the NCI (1978) feeding studies in male and<br />

female F344 rats and B6C3F 1 mice, and the feeding study by Evarts and Brown (1980) in female F344<br />

rats. Cancer potency is based on dose-response data for benign and malignant thyroid tumors in male<br />

rats, the most sensitive sex and species (see Table 1) (Cal/EPA, 1992).<br />

Methodology<br />

Expedited Proposition 65 methodology (with cross-route extrapolation) was used to derive a cancer<br />

potency factor. A unit risk factor was then calculated by <strong>OEHHA</strong>/ATES from the cancer potency<br />

factor using a reference human body weight of 70 kg and an inspiration rate of 20 m 3 /day.<br />

V. REFERENCES<br />

California Environmental Protection Agency (Cal/EPA) 1992. Expedited Cancer Potency Values and<br />

Proposed Regulatory Levels for Certain Proposition 65 Carcinogens. Office of Environmental Health<br />

Hazard Assessment, Reproductive and Cancer Hazard Assessment Section, Berkeley, CA.<br />

Evarts RP and Brown CA. 1980. 2,4-diaminoanisole sulfate: early effect on thyroid gland morphology<br />

and late effect on glandular tissue of Fischer 344 rats. J Natl Cancer Inst 65:197-204.<br />

Gold L, Sawyer C, Magaw R, Backman G, de Veciana M, Levinson R, Hooper N, Havender W,<br />

Bernstein L, Peto R, Pike M and Ames B. 1984. A Carcinogenic Potency Database of the<br />

standardized results of animal bioassays. Environ Health Perspect 58:9-319.<br />

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