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Table 4.<br />

Derivation of cancer potencies from NCI (1979) and Innes et al.(1969).<br />

study tumor/group q 1<br />

*<br />

(mg/kg-day) -1<br />

q animal (mg/kgday)<br />

-1<br />

q human (mg/kgday)<br />

-1<br />

maximum<br />

likelihood<br />

estimate<br />

LCB<br />

(95%)<br />

NCI, hepatoma/ 0.0017 12.1 0.021 0.016 0.004<br />

1979 male<br />

hepatoma/ 0.0006 12.6 0.008 0.003 0<br />

female<br />

Innes, reticulum cell 0.035 0.035 0.47 0.2 0.05<br />

1969 sarcoma/ male<br />

hepatoma/ 0.021 0.021 0.28 0.11 0.03<br />

female<br />

LCB = Lower confidence bound.<br />

The highest upper bound cancer potency for humans (q human ) was derived from the results of the Innes<br />

et al. (1969) study showing reticulum cell tumor induction in male B6C3F 1 mice. However, confidence<br />

in this value is reduced because the number of animals used in the study is small (18/group) and data<br />

were reported incompletely. Innes et al. (1969) and NCI (1979) both present data showing induction<br />

of hepatomas in female B6C3F 1 mice. However, lack of overlap between the 95% confidence bounds<br />

of the two potencies suggests there may be a greater sensitivity to this effect in the strain used by Innes<br />

et al (1969). Selection of a cancer potency value is made based on the most sensitive species, site, and<br />

study in the absence of evidence indicating the value is not representative (CDHS, 1985). On balance,<br />

the evidence favors neither the higher sensitivity of the Innes et al. (1969) study nor the high quality of<br />

the NCI (1979) study. For this reason, a method of Anderson (1983) was chosen for combining the<br />

results of these studies. The resulting cancer potency derived from the geometric mean of the four<br />

potencies shown in Table 4 is 0.07 (mg/kg-day) -1 .<br />

A unit risk value based upon air concentrations was derived by <strong>OEHHA</strong>/ATES using an assumed<br />

human breathing rate of 20 m 3 /day, 70 kg human body weight, and 100% fractional absorption after<br />

inhalation exposure. The calculated unit risk value is 2.0 E-5 (µg/m 3 ) -1 .<br />

V. REFERENCES<br />

Anderson EL and the U.S. Environmental Protection Agency Carcinogen Assessment Group. 1983.<br />

Quantitative approaches in use to assess cancer risk. Risk Anal 3:277-295.<br />

Armitage P and Doll R. 1954. The age distribution of cancer and a multistage theory of carcinogenesis.<br />

Br J Cancer 3:1-12.<br />

535

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