The discussion on whether the Sprague Dawley (SD), the Fischer F344, or the Hannover Wistar rat is the most appropriate model for toxicity studies in rodents is ongoing. A substantial quantity of data on these strains concerning their source, diet, and housing conditions have been published. Generally, before starting a toxicology program in rodents, it should be taken into account that oncogenicity studies will be required for the majority of compounds successfully completing development. Survival, body weight development, incidence, type, time of onset of age-dependent lesions and neoplasms, as well as some special considerations of the rat model selected may be decisive. Therefore, an understanding of the historical background data is essential. These aspects demonstrate why the use of a specific rat model should be carefully considered at the beginning of the toxicology program.
A total of 1170 rats comprised of 65 male and 65 female Han Wistar rats per group were exposed for 2 h/day, 5 days/ week for up to 104 weeks to GSM or DCS wireless communication signals at three nominal SARs of 0.44, 1.33 and 4.0 W/kg. A preliminary study confirmed that the highest exposure level was below that which was capable of causing a measurable increase in the core temperature of the rat. Additional groups for each modulation were sham exposed, and there was also an unrestrained, unexposed (cage) control group. Fifteen male and 15 female rats per group were killed after 52 weeks. From the remaining 50 male and 50 female rats per group, surviving animals were killed after 104 weeks. Evaluations during the study included mortality rate, clinical signs, recording of palpable masses, body weight, food consumption, ophthalmoscopic examination, and clinical pathological investigations. Terminal investigations included organ weight measurement and macroscopic and microscopic pathology examinations. There was no adverse response to the wireless communication signals. In particular, there were no significant differences in the incidence of primary neoplasms, the number of rats with more than one primary neoplasm, the multiplicity and latency of neoplasms, the number of rats with metastases, and the number of benign and malignant neoplasms between the rats exposed to wireless communication signals and rats that were sham exposed.
Inhalation of vanadium pentoxide clearly increases the incidence of alveolar/bronchiolar neoplasms in male and female B6C3F1 mice at all concentrations tested (1, 2 or 4 mg/m3), whereas responses in F344/N rats was, at most, ambiguous. While vanadium pentoxide is mutagenic in vitro and possibly in vivo in mice, this does not explain the species or site specificity of the neoplastic response. A nose-only inhalation study was conducted in female B6C3F1 mice (0, 0.25, 1 and 4 mg/m3, 6 h/day for 16 days) to explore histopathological, biochemical (α-tocopherol, glutathione and F2-isoprostane) and genetic (comet assays and 9 specific DNA-oxo-adducts) changes in the lungs. No treatment related histopathology was observed at 0.25 mg/m3. At 1 and 4 mg/m3, exposure-dependent increases were observed in lung weight, alveolar histiocytosis, sub-acute alveolitis and/or granulocytic infiltration and a generally time-dependent increased cell proliferation rate of histiocytes. Glutathione was slightly increased, whereas there were no consistent changes in α-tocopherol or 8-isoprostane F2α. There was no evidence for DNA strand breakage in lung or BAL cells, but there was an increase in 8-oxodGuo DNA lesions that could have been due to vanadium pentoxide induction of the lesions or inhibition of repair of spontaneous lesions. Thus, earlier reports of histopathological changes in the lungs after inhalation of vanadium pentoxide were confirmed, but no evidence has yet emerged for a genotoxic mode of action. Evidence is weak for oxidative stress playing any role in lung carcinogenesis at the lowest effective concentrations of vanadium pentoxide.
Hexamethyldisiloxane (HMDS) is a volatile linear siloxane dimer used in many applications, including precision cleaning, active ingredient carrier, and as a manufacturing intermediate. The purpose of this study was to characterize the subchronic vapor inhalation toxicity of the material as part of a comprehensive toxicology program. Groups of 20 male and 20 female Fischer 344 (F344) rats were exposed to nominal (and mean actual) vapor concentrations of 0, 50 (50), 200 (194), 600 (593), 1,500 (1,509) and 5,000 (5,012) ppm of HMDS, 6 hours per day, 5 days per week, for 13 weeks. No treatment-related signs of clinical toxicity or mortality, statistically significant effects upon body weight gain or food consumption, ophthalmoscopic changes, gross macroscopic necropsy findings, or organ weight changes were noted. Minor hematological, clinical biochemical, and urinalysis changes were seen but were not considered to be of toxicological relevance. Histological lesions in the kidney apparently consistent with male rat-specific alpha-2-urinary globulin nephropathy were observed in male rats exposed to 593, 1,509, and 5,012 ppm of HMDS, accompanied by slightly increased plasma urea and creatinine concentrations. No other treatment-related histological changes were seen in HMDS-exposed rats.
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