Rat two-generation reproduction and dominant lethal study of acrylamide in drinking water.

Fischer 344 (F344) F(0) weanling rats, 30/sex/group, were exposed to acrylamide in drinking water at 0.0, 0.5, 2.0, or 5.0 mg/kg/day for 10 weeks and then mated. Exposure of F(0) females continued through gestation and lactation of F(1) litters. F(0) males, after F(0) mating, were removed from exposure and mated (one male: two untreated females) for the dominant lethal (DL) assay. Thirty F(l) weanlings/sex/group were exposed for 11 weeks to the same dose levels as their parents, and then mated to produce F(2) offspring. F(0) and F(l) parents and F(1) and F(2) weanlings were necropsied. Prebreeding exposure of F(0) and F(l) animals resulted in systemic toxicity at 2.0 to 5.0 mg/kg/day, with head tilt and/or foot splay increased at 0.5 to 5.0 mg/kg/day. F(0) and F(l) reproductive indices and gestational length were unaffected. Implantations and live pups/litter at birth were reduced at 5.0 mg/kg/day. Survival of F(l) and F(2) pups was reduced at 5.0 mg/kg/day for PND 0 through 4 only. In the DL assay, total and live implants were reduced, pre- and postimplantation loss was increased, and the frequency of DL factors (F(L)%) was increased at 5.0 mg/kg/day. At 5.0 mg/kg/day, adult F(l) male peripheral nerves exhibited axonal fragmentation and/or swelling; F(l) female spinal cord sections were unremarkable. The NOEL for prenatal DL was 2.0 mg/kg/day; the NOEL for adult systemic toxicity, including neurotoxicity, was < or = 0.5 mg/kg/day. Therefore, neurotoxicity and DL were differentially affected.

Chronic toxicity and oncogenicity study on acrylamide incorporated in the drinking water of Fischer 344 rats.

Male and female Fischer 344 rats were maintained on treated drinking water providing dosages of 0 (controls), 0.01, 0.1, 0.5, or 2.0 mg acrylamide/kg body wt/day for 2 years to assess the chronic toxicity and oncogenic potential of the chemical. The mean body weights of male and female rats receiving 2.0 mg/kg/day and of male rats receiving 0.5 mg/kg/day were minimally decreased when compared with controls. During the last 4 months of the study, there was an increase in mortality among male and female rats receiving 2.0 mg/kg/day. A target organ effect, characterized by degeneration of peripheral nerves, was observed in rats receiving 2.0 mg/kg/day. The incidence of several tumor types was increased in the rats receiving 2.0 mg/kg/day when compared with controls. In females, increased tumor incidences were observed in the mammary gland, central nervous system, thyroid gland-follicular epithelium, oral tissues, uterus, and clitoral gland. In males the incidence of tumors of the thyroid gland-follicular epithelium and scrotal mesothelium was increased. Male rats receiving 2.0 mg/kg/day also had increased incidence of central nervous system tumors when compared to historical controls but not when compared to concurrent controls. The only tumor incidence which was significantly increased at the 0.5 mg/kg/day level was scrotal mesothelioma. There was no statistically significant increase of any tumor type at the 0.1 or 0.01 mg/kg/day dose levels. However, the incidence of scrotal mesothelioma at the 0.1 mg/kg/day level was greater than that observed in the control group or historically reported in this laboratory.