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Table 1 (continued):<br />

Chloroform carcinogenicity bioassay tumor incidence data used to estimate<br />

cancer potency (CDHS, 1990)<br />

Study Strain/Species Sex Tumor Site Lifetime Daily Dose<br />

(mg/kg-day)<br />

Tumasonis<br />

et al. (1985)<br />

Reuber et al.<br />

(1979) using<br />

NCI (1976)<br />

Wistar rat F cholangiocarcinoma control<br />

220<br />

Wistar rat M cholangiocarcinoma control<br />

160<br />

Osborne-Mendel rat F cholangiocarcinoma and<br />

cholangiofibroma<br />

a<br />

toothpaste base was used as the vehicle; b arachis oil was used as the vehicle<br />

control<br />

50<br />

100<br />

Tumor<br />

Incidence<br />

0/18<br />

34/40<br />

0/22<br />

17/28<br />

0/20<br />

3/39<br />

11/39<br />

IV.<br />

DERIVATION OF CANCER POTENCY<br />

Basis for Cancer Potency<br />

Chloroform is carcinogenic to rats and mice (NCI, 1976; Roe et al., 1979; Jorgenson et al., 1985).<br />

The International Agency for Research on Cancer (IARC) has classified chloroform as a possible<br />

human carcinogen (Group 2B). Similarly, the U.S. EPA has placed chloroform in Group B2 in their<br />

classification scheme, based on sufficient evidence of carcinogenicity in animals, but inadequate<br />

epidemiologic evidence. Current evidence and understanding of the carcinogenic process is insufficient<br />

to classify chloroform as either a genotoxic or epigenetic carcinogen, and it is possible that both types of<br />

effects are involved.<br />

The estimation of cancer risk to humans from exposure to chloroform by CDHS (1990) is based on<br />

animal studies. Data were chosen based primarily on statistical significance, as discussed below.<br />

Methodology<br />

The following data sets were evaluated to estimate chloroform cancer potency: 1) Liver tumor data in<br />

male and female B6C3F 1 mice, and renal tubular cell tumors in male Osborne-Mendel rats from the<br />

NCI (1976) study were chosen because statistically significant increases in these tumor types were<br />

observed in chloroform treated animals relative to controls; 2) Renal tubular cell tumor data in male<br />

Osborne-Mendel rats from the Jorgenson et al. (1985) study and in male ICI mice in the Roe et al.<br />

(1979) study were used for risk estimation based on a statistically significant increase in kidney tumors<br />

in chloroform treated animals relative to controls; 3) Liver cholangiocarcinoma ("adenofibrosis”) data in<br />

female rats from Tumasonis et al. (1985), and from Reuber's reanalysis of the NCI (1976) slides<br />

(Reuber, 1979) were also analyzed with the linearized multistage model (GLOBAL86). Administered<br />

doses were transformed to lifetime doses by adjusting for the number of days exposed per week and<br />

the ratio of the length of exposure to the length of the experiment (exposure plus observation period).<br />

197

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