Dioxin and certain structurally related compounds increase the incidence of liver neoplasms in rodents upon chronic bioassay. Short-term studies indicate the lack of direct DNA-damaging e ects including covalent binding to DNA; however, secondary mechanisms may be important in the observed carcinogenicity as these chemicals a ect a number of pathways necessary for maintenance of normal growth control and di erentiation status. Studies with TCDD in the mouse skin support a lack of initiating activity but an ability to promote the growth of previously initiated lesions indicative of a promoting agent. Mouse skin tumour promotion studies indicate that Ah receptor activation may be involved in promotion by TCDD and selected structurally related compounds. While the mechanism of carcinogenicity induced by TCDD is unknown, the processes involved have a no-e ect level, which in the rat liver is at an exposure level below 10 ng TCDD/kg/ day. At least for the rodent liver, the relative e ective dose for cytochrom e P450 induction is not a good indicator of promotion potency. Studies on liver tumour promotion in the female rat liver support a nongenotoxic mechanism for the induction of neoplasms by TCDD. The ability of TCDD to enhanc e proliferation and inhibit apoptoti c processes in focal hepatic lesions further supports an indirect mechanism of carcinogenicity.Carcinog enicity studies with TCDD Kociba et al. (1978) performed a lifetime feeding study with 1, 10, and 100 ng TCDD/kg/day to male and female Sprague± Dawley rats. The results of the 2-year bioassay on the incidence of tumours induced by feeding TCDD to Sprague± Dawley rats form the primary basis for the regulatio n of TCDD as a known animal carcinogen and possible human carcinogen (IARC 1987). The female rat liver was the primary target site as assessed by a Dow Chemical Co. pathologist and independently by R. Squire (Kociba et al. 1978). The Kociba study demonstrat ed hepatic hyperplastic nodules at an incidence of 8/86, 3/50, 18/50, and 23/50 for control, 1, 10, and 100 ng/kg/day respectively. Similarly, the incidence of hepatocellular carcinomas in female rats was 1/86, 0/50, 2/50, and 11/50 for these treatmen t groups from dietary levels of backgroun d, 22, 210, and 2200 ppt, respectively, for these groups. Since the criteria for assessment of hepatic lesions had evolved after the original determination , a re-evaluati on of the hepatoproliferative lesions in the female rat liver of TCDD-treated animals was performed by the Pathology Working group (Goodman and Sauer 1992). This re-evaluation detected a similar trend for hepatic tumour incidence as previously reported (Kociba et al. 1978), but a lower incidence was noted in the re-evaluation than in the original study; however, a clear increase in the incidence of combined liver tumours (adenomas and carcinomas) was observed in the middle (9/50) and high dose (14/50) groups compared with the control (2/86). Four hepatocellular carcinomas were observed and these were well di erentiated, while the majority ...