Spontaneous renal tumors in two rats from a thirteen week rodent feeding study with grain from molecular stacked trait lepidopteran and coleopteran resistant (DP-ØØ4114-3) maize.

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. An expert panel of pathologists was convened as a Pathology Working Group (PWG) to review coded kidney histology sections from control (091) and treated (4114 and 4114GLU) male rats. The objectives were for the panel to characterize the histopathologic findings and to interpret their relationship to consumption of the indicated diet. The PWG concluded unanimously that the kidney tumors were characteristic of amphophilic-vacuolar (AV) tumors and AV atypical tubular hyperplasia which represent a distinctive phenotype that has been reported to occur sporadically in young Sprague Dawley Rats. The PWG determined that the neoplasms and atypical tubular hyperplasias were multicentric and bilateral which typifies tumors of familial origin. Degenerative/regenerative or cytotoxic changes consistent with nephrotoxicity leading to tumor induction were not observed in these rats and thus supports the conclusion that tumors were unrelated to consumption of the test diet. It was the unanimous opinion of the PWG that the proliferative renal tubule cell lesions were spontaneous and not related to consumption of diets containing 4114 maize grain.

Morphological characterization of the ovary under normal cycling in rats and its viewpoints of ovarian toxicity detection.

Identification 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. Transversely dissected maximum areas in the ovaries were examined microscopically for the two major features, follicles and corpora lutea (CL). Classification of growing follicles was in reference to Pedersen and Peters (1968), and functionally divided into follicular stimulating hormone (FSH)-independent and dependent categories. The former, small and medium-sized follicles, respectively primordial/primary and preantral follicles, could be readily detected by immunohistochemical staining for proliferating cell nuclear antigen (PCNA). The large antral and Graafian follicles and large sized atretic follicles showed sequential changes depending on the estrous cycle stage. CL could be divided into currently and previously formed examples. Currently formed CL underwent remarkable changes in their appearance with the cycle, reflecting ovulation and progesterone production. Thus morphological analysis that is synchronized the large antral follicle changes with recently formed CL ones allows the ovary to be classified into the each estrous cycle stage. Morphological deviation from any synchronized combination provides a first pointer of ovarian toxicity. PCNA immunohistochemical staining is also useful to detect small follicles.

Kojic acid -absence of tumor-initiating activity in rat liver, and of carcinogenic and photo-genotoxic potential in mouse skin.

Kojic 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. In medium-term carcinogenesis test in rats, 2.0% KA was orally given to F344/DuCrj rats for 4 weeks of the initiation period, followed by the combination of partial hepatectomy and treatment with a hepatocarcinogenesis promoter, phenobarbital (PB). As a result, glutathione S-transferase placental form (GST-P) positive foci of 0.2 mm or more in diameter in the KA group, which is usually used in determination of pre-cancerous lesions, did not increase significantly in both numbers and areas compared with those of the non-initiated controls. In the concurrent analysis, however, numbers of GST-P-positive foci of two cells or more and 0.1 mm or more in diameter increased slightly, and possible weak initiation activity of KA was equivocal. However, considering the known fact that KA exerts promotion activity in the liver of F344 rats by long-term dietary administration, it was suggested that the observed slight increase of the numbers of GST-P-positive foci in rat liver was the effect of promotion activity of KA rather than the initiation activity. In DNA adducts formation assay in a rat liver, no clear adducts derived from KA were detected in male F344/DuCrj rats administered 0.5% or 2% KA orally, and KA was considered not to form DNA adducts in rat liver. In the in vitro photo-reverse mutation assay with bacteria, KA exerted weak photo-mutagenicity. Furthermore, in chromosome aberration study in Chinese hamster lung cells (CHL/IU cells) with UV irradiation, KA induced chromosome aberration at high-dose (1.4 mg/mL) treatment with UV irradiation, but was negative without UV irradiation. However, in the in vivo photo-micronucleus study in mouse, in which 1.0 or 3.0% KA containing cream was applied twice to the back of the animals with a 24-hr interval, KA did not induce micronuclei in mouse epidermal cells. Based on these results, it is considered that the risk of KA to exert photo-carcinogenicity is quite low in the skin. In skin carcinogenesis bioassay for initiation-promotion potential, 3.0% KA cream formulation was applied to the back of the mouse for 1 week (once a day, total 7 times) and for 19 weeks (5 times a week, total 95 times) during the initiation and the promotion stages, respectively. No skin nodules were observed in any animal skins formed due to KA treatment given in either stage. Therefore, KA is considered not to possess initiation nor promotion activity of skin carcinogenesis. Furthermore, from the above findings, it is suggested that KA is virtually safe as a quasi-drug ingredient.

Two-generation reproductive toxicity studies in rats with extra parameters for detecting endocrine disrupting activity: introductory overview of results for nine chemicals.

Two-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.