Food Chem Toxicol
March 2013
A thirteen week feeding study was conducted by feeding young adult male and female Sprague Dawley [Crl:CD®(SD)] rats diets containing grain from genetically modified (GM) DP-ØØ4114-3 maize that was either untreated (4114) or treated in the field with glufosinate ammonium (4114GLU). Control rats were fed diets containing the same concentration of near isogenic, non-GM maize grain (091) or one of three types of commercially available non-GM maize grain. At the end of the in-life phase, renal tubule tumors were reported in two male rats consuming diets containing 4114 maize grain.
View Article and Find Full Text PDFIdentification of ovarian toxicity is very important for safety assessment of drugs and other environmental chemicals. The detection of interference with ovarian function is very hard without a thorough understanding of the normal ovarian morphology based on reproductive physiology. The focus of the present study was therefore a practical analysis in each stage of the estrous cycles using ovaries obtained from 143 rats demonstrating normal cycling.
View Article and Find Full Text PDFKojic acid (KA) has been widely used as a quasi-drug ingredient. Possible promotion activity of KA was suggested on livers of mouse and rat by findings obtained in genotoxicity and carcinogenicity studies performed thus far. Therefore, in order to examine safety as a quasi-drug ingredient, we investigated the presence of initiation activity in rat liver and the photo-genotoxicity and carcinogenicity in mouse skin.
View Article and Find Full Text PDFTwo-generation reproductive toxicity studies using rats of benzophenone, n-butylbenzene, butyl benzyl phthalate, 2,4-dichlorophenol, dicychlohexyl phthalate, diethyl phthalate, 4-nitrotoluene, lindane and vinclozolin, were performed to investigate whether these chemicals have endocrine-mediated effects with the support of the Ministry of Economy, Trade and Industry and the Ministry of the Environment. Benzophenone exposure was via the diet at concentrations of 0, 100, 450 or 2000 ppm, n-butylbenzene was administered orally by gavage at dose levels of 0, 30, 100 or 300 mg/kg/day, butyl benzyl phthalate was administered orally by gavage at dose levels of 0, 100, 200, or 400 mg/kg/day, 2,4-dichlorophenol was administered in the diet at concentrations of 0, 500, 2000 or 8000 ppm, dicyclohexyl phthalate was given in the diet at concentrations of 0, 240, 1200 or 6000 ppm, diethyl phthalate was administered in the diet at concentrations of 0, 600, 3000 or 15000 ppm, 4-nitrotoluene was administered orally by gavage at doses of 0, 40, 80, or 160 mg/kg/day, lindane exposure was in the diet at concentrations of 0, 10, 60, or 300 ppm, and vinclozolin treatment was by feeding diet at concentrations of 0, 40, 200 or 1000 ppm.
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