Risk assessment of 2,3,7,8-TCDD using a biologically based cancer model: a reevaluation of the Kociba et al. bioassay using 1978 and 1990 histopathology criteria.
The Moolgavkar-Venzon-Knudson (M-V-K) two-stage model for carcinogenesis was used to estimate the risk-specific dose (RsD) based on the incidence of tumors reported by Kociba et al. (1978) for Sprague-Dawley rats exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin (2,3,7,8-TCDD; dioxin). The results from the recently completed (1990) reevaluation of the Kociba et al. study, which used the current National Toxicology Program (NTP) pathology criteria, were also evaluated. Time-to-tumor information for each rat was incorporated into the analysis. Model parameters for the approximate form of the hazard function of the two-stage M-V-K model were determined by maximum likelihood estimation. This simplification was significant but necessary, because laboratory data on the intermediate cell growth rate and the transition rates have not been determined. Estimates of the RsD (10(-6) risk) (based on the original 1978 histopathology results) were 10 fg/kg/d when carcinomas and hyperplastic nodules were combined and 150 fg/kg/d when only carcinomas were considered. In contrast, using the 1990 histopathology data, the RsD (10(-6) risk) was 80 fg/kg/d when adenomas and carcinomas were combined and 25,000 fg/kg/d when only hepatocellular carcinomas were considered. Since the two-stage M-V-K model is intended to predict the occurrence of malignant tumors, the mathematically appropriate RsD is 25,000 fg/kg/d (10(-6) risk). Because the model does not account for pharmacokinetics or the possibility of other toxic effects, the appropriate RsD (10(-6) risk) for humans should be much smaller. Using the carcinoma data only, a sensitivity analysis of key parameters in the model was conducted. Results indicated that the ranges of plausible values for the RsD (10(-6) risk) for the original 1978 and the 1990 reevaluation data were 70-2600 fg/kg/d and 120-50,000 fg/kg/d, respectively. The lowest plausible RsD is, therefore, approximately 10-fold greater than the current U.S. EPA RsD (10(-6) risk) of 6.4 fg/kg/d [which is based on the linearized multistage (LMS) model]. Even though these results must be considered preliminary until some of the values for the model parameters are experimentally determined and a complete physiologically based or receptor-based model is developed, this analysis shows that nearly any plausible laboratory data on tumor progression will yield a much higher RsD than currently embraced by the U.S. EPA.
Paustenbach
D J
DJ
ChemRisk Division of McLaren/Hart, Alameda, California.
Layard
M W
MW
Wenning
R J
RJ
Keenan
R E
RE
D000818:Animals; D001681:Biological Assay; D015197:Carcinogenicity Tests; D006528:Carcinoma, Hepatocellular / Q000139:chemically induced* / Q000453:epidemiology; D016009:Chi-Square Distribution; D004305:Dose-Response Relationship, Drug; D005260:Female; D015994:Incidence; D008113:Liver Neoplasms / Q000139:chemically induced* / Q000453:epidemiology; D008297:Male; D000072317:Polychlorinated Dibenzodioxins / Q000633:toxicity*; D011336:Probability; D051381:Rats; D011919:Rats, Inbred Strains; D012307:Risk Factors
D000072317:Polychlorinated Dibenzodioxins