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  • Title: Oncogenicity studies of inhaled methyl tertiary-butyl ether (MTBE) in CD-1 mice and F-344 rats.
    Author: Bird MG, Burleigh-Flayer HD, Chun JS, Douglas JF, Kneiss JJ, Andrews LS.
    Journal: J Appl Toxicol; 1997 May; 17 Suppl 1():S45-55. PubMed ID: 9179727.
    Abstract:
    Oncogenicity studies of methyl tertiary-butyl ether (MTBE) vapor were conducted in CD-1 mice and Fischer 344 rats. Fifty animals of each sex per species per group were exposed for 6 h a day, 5 days per week to 0 (control), 400, 3000 and 8000 ppm MTBE vapor in air for 18 months (mice) and 24 months (rats). Both species showed reversible central nervous system depression at 8000 ppm for the first week of exposure, which continued for mice for the study duration. For the 8000 ppm mice, reduced body weight gain and early mortality prior to terminal euthanasia were exposure related. In the males, these deaths appear to be due to exacerbation of uropathy or dysuria, which occurs spontaneously in this strain. Increases in absolute and relative liver (both sexes) and kidney weight (males only) were seen at 3000 and 8000 ppm and decreases in brain and spleen weights were also noted (the latter decreases were without microscopic lesions and occurred at 8000 ppm only). An increase in hepatocellular hypertrophy occurred in both sexes at the two highest concentrations. The only neoplastic lesion found in this study in mice was an increased incidence of hepatocellular adenomas in females at the 8000 ppm exposure. In a follow-up study, a statistically significant elevation of cell proliferation in female mouse liver has been shown to occur following 5 days, but not 28 days, of exposure to 8000 ppm MTBE, suggesting that MTBE induces mitogenesis. For male rats, early euthanasia was required at week 82 and week 97 for the 8000 and 3000 ppm groups, respectively, due to excessive mortality from a severe progressive nephrosis. The end stage of this process appeared earlier in the male rats of all MTBE exposure groups; the incidence of this lesion and mortality for exposed females was comparable to control females. No exposure-related changes in hematological parameters were observed for any group at any time point, but a decrease in corticosterone levels was seen for male rats from the 8000 ppm group. Absolute and relative kidney and liver weight increases occurred in 3000 and 8000 ppm exposure groups, but the liver weight change was not accompanied by histopathological change. At study termination, increases in the incidence and severity of a chronic nephropathy in males from all exposure groups and in females exposed to 3000 and 8000 ppm was associated with secondary lesions of hyperplasia of the parathyroid and mineralization of tissues. Renal tubular cell tumors were increased in male rats exposed to 3000 and 8000 ppm. This may be associated with an accumulation of protein (stainable by Mallory's Heidenhain) in kidney tubular epithelial cells after 4 weeks of exposure. An increased incidence of interstitial cell adenomas of the testes was seen in males exposed to 3000 and 8000 ppm but was believed to be an artefact of an unusually low control incidence and not considered to be exposure related. Based on the above effects, the no-observed-effect level (NOEL) for chronic toxicity is 400 ppm, and the NOEL for carcinogenic effects is 3000 ppm (mice) and 400 ppm (rats).
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