All rats survived to the end of the study. The final mean body weights of exposed rats were within 10% of those of the untreated and vehicle controls. Feed consumption by exposed groups of male and female rats was similar to that by the control groups, suggesting that the diet was palatable to the animals. Based on average feed consumption values, male rats ingested approximately 300, 600, 1,200, 2,400, or 4,800 mg 1,1,1-trichloroethane/kg body weight per day, and females received 300, 650, 1,250, 2,500, or 5,000 mg/kg per day. In general, changes in clinical pathology parameters were minor, sporadic, and inconsistent between males and females; these differences were not considered to be treatment related or biologically significant. The liver weights of female rats administered 80,000 ppm were significantly less than those of the untreated and vehicle controls. Male rats exposed to 10,000 ppm or greater had a spectrum of nonneoplastic kidney lesions consistent with hyaline droplet nephropathy. No treatment-related gross or microscopic lesions were observed in female rats.
There were no exposure-related deaths in mice. Based on average feed consumption values, male mice ingested approximately 850, 1,770, 3,500, 7,370, or 15,000 mg/kg per day, and female mice received 1,340, 2,820, 5,600, 11,125, or 23,000 mg/kg per day. Even though feed consumption by exposed groups was slightly greater than that by the controls, the mean body weights of male and female mice administered 20,000 ppm or greater were significantly less than those of the untreated and vehicle controls. The heart, kidney, and lung weights of the vehicle control male mice were significantly greater than those of the untreated controls. There were no biologically significant differences in organ weights between exposed and control mice. No gross or microscopic lesions in male or female mice were attributed to chemical exposure.
Epididymal spermatozoal concentrations of male rats and mice given 80,000 ppm were significantly less than those of the vehicle controls.
1,1,1-Trichloroethane was not mutagenic in Salmonella typhimurium strains TA98, TA100, TA1535, or TA1537, with or without S9 metabolic activation. In the mouse lymphoma assay for induction of trifluorothymidine resistance in L5178Y cells, 1,1,1-trichloroethane gave a negative response in one test (with and without S9) and an equivocal response in a second test (in the presence of S9). Results of a sister chromatid exchange test in cultured Chinese hamster ovary cells were considered to be equivocal due to an unrepeated questionable response obtained in the presence of S9 in a single trial; without S9, results were negative. 1,1,1-Trichloroethane induced chromosomal aberrations in cultured Chinese hamster ovary cells in the absence of S9; with S9, the increase in aberrations noted in a single trial was not significant. A small increase in the frequency of micronucleated normochromatic erythrocytes was noted in peripheral blood slides from male mice administered 1,1,1-trichloroethane in feed for 13 weeks; the results were determined to be equivocal, while the female peripheral blood micronucleus test results were negative.
In conclusion, 1,1,1-trichloroethane induced nonneoplastic lesions consistent with hyaline droplet nephropathy in male rats. Exposure to 1,1,1-trichloroethane caused decreases in liver weights in female rats and decreases in mean body weights of male and female mice. The no-observed-adverse-effect level (NOAEL) was estimated to be 10,000 ppm for male and female rats and mice.
Synonyms: Chloroethene; methylchloroform; methyl trichloromethane; -trichloroethane; 1,1,1-TCE
Report Date: August 2000
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