Subacute oral and dermal toxicity of tert-butyl hydroperoxide in Fischer F344/N rats and B6C3F1 mice

Tert-butyl hydroperoxide (TBHP) is a catalyst frequently used in oxidation and sulfonation reactions in the plastics industry. Since the toxicological evaluation of TBHP remains unknown, the National Toxicology Program (NTP) designed studies to characterize and compare TBHP toxicity by the dermal and oral (gavage) routes in male and female Fischer 344 rats and B6C3F1 mice in 14-day exposures. Rats and mice were administered TBHP at 22, 44, 88, 176 or 352 mg/kg in 0.5% aqueous methylcellulose for the gavage studies. In the dermal studies, mice were administered the same doses as above, while rats were administered four doses (22, 44, 88, 176 mg/kg) in 50% aqueous acetone. Results from the gavage studies revealed treatment-related decreases in survival in male rats and body weights in both male and female rats in the 352 mg/kg group. Clinical signs included post-treatment lethargy, thinness, abnormal breathing, ruffled fur, and/or ataxia which occurred sporadically. The male mice showed a statistically significant decrease in body weight in the 44, 88, 176, and 352 mg/kg groups. The major target organs of toxicity were the forestomach in male and female rats and mice, and the esophagus in male and female rats and in male mice. In addition, there was an increase in the absolute and relative liver weight in female mice with hepatocellular hypertrophy in the top-dose group only. Results from spin trapping experiments revealed the presence of electron paramagnetic resonance signals from radical adducts in the blood and organic extracts of the liver and kidneys of rats treated by gavage with 176 mg/kg TBHP, suggesting the involvement of free- radical generation. The no observed adverse effect level (NOAEL) was considered to be 22 mg/kg in rats and male mice, and 44 mg/kg in female mice. In the dermal studies, there was no effect on survival, body weight, or organ weights in either rats or mice. TBHP administration at the site of application resulted in dermal irritation, hyperkeratosis, hyperplasia, and/or inflammation of the epidermis and inflammation of the dermis at 176 mg/kg and above in male and female rats. Dermal irritation at the site of application was noted in all the mice exposed to 352 mg/kg TBHP. Histopathological lesions in the epidermis and dermis were seen in the 88-352 mg/kg males and in the 176-352 mg/kg females. The NOAEL was found to be 88 mg/kg for male rats and female mice, and 44 mg/kg for female rats and male mice. In conclusion, these studies demonstrate that TBHP is metabolized to free radicals and is a contact irritant affecting skin by the dermal route of exposure, and forestomach and esophagus by oral administration. There was no evidence of systemic absorption by the dermal route of exposure based on lack of pathological findings (Supported by National Institute of Environmental Health Sciences Contract No. N01-ES-65406).     

Prechronic Toxicity Studies on 2-Ethylhexanol in F334 Rats and B6C3F1 Mice

Data on the subchronic toxicity of 2-ethylhexanol (2EH) wererequired to establish the dose vehicle and dose levels for oncogenicitystudies. In preliminary studies 2EH was given subacutely (11days) to male and female Fischer 344 rats and B6C3F1 mice asan aqueous emulsion by oral gavage (0, 100, 330, 1000, and 1500mg/kg/day). Clinical observations were made, body weights, foodconsumption, clinical chemistries, hematologies, and selectedorgan weights were measured, and gross and micropathologieswere performed. Target organs were the central nervous system,liver, forestomach, spleen, thymus, and kidney in rats and thecentral nervous system, liver, and forestomach in mice. 2EHwas then administered by oral gavage to male and female F344rats and B6C3F1 mice as an aqueous emulsion (0, 25, 125, 250,and 500 mg/kg/day) for 13 weeks. At 500 mg/kg/day in the ratthere was reduced body weight gain (6% male, 7% female), increasedrelative liver (29% male, 15% female), kidney (16% male, 6%female), stomach (11% male, 16% female), and testes (6%) weights,and moderate gross and microscopic changes in the liver andforestomach. There were no behavioral effects or effects onthe spleen or thymus. A no-effect level for target organ effectsin the rat was 125 mg of 2EH/kg/day. At 500 mg of 2EH/kg/dayin the mouse the only effects were increased relative stomachweights in males (13%) and a low incidence of gross and microscopicfindings in the forestomach (male and female) and liver (female).A no-effect level for target organ effects in the mouse was125 mg of 2EH/kg/day. 2EH was a peroxisome proliferator in therat but not in the mouse at subchronic dose levels of 500 mg/kg/day.Dose levels in oncogenicity studies were set at 50 mg/kg/dayfor the absence of treatment-related effects in rats and mice,and 500 and 750 mg/kg/day, respectively, in rats and mice ashigh doses producing minimal toxicity without altering the lifespan.     

Forestomach tumor induction by 2,4-hexadienal in F344N rats and B6C3F1 mice

2,4-Hexadienal (2,4-Hx) was studied for its toxicity and carcinogenicity because of its , -unsaturated aldehyde structure and potential link between exposure to lipid peroxidation products in the diet and human malignancies. Male and female F344N rats and B6C3F1 mice received 2,4-Hx in corn oil by gavage for 16 days, 14 weeks, or 2 years. In the 16-day studies 2,4-Hx induced forestomach necrosis and ulceration at 240 mg/kg and forestomach epithelial hyperplasia at 80 mg/kg in rats and mice. In the 14-week studies the chemical induced forestomach hyperplasia and nasal olfactory atrophy or necrosis at 120 mg/kg in rats and mice. In the 2-year studies 2,4-Hx induced squamous cell papilloma and carcinoma of the forestomach in male and female rats at 45 and 90 mg/kg and in male and female mice at 120 mg/kg. Two male mice in the 120 mg/kg group had uncommon squamous cell carcinoma of the oral cavity (tongue). Mechanistic studies indicated that the forestomach carcinogenesis in rats and mice may be due to depletion of glutathione as a result of oxidative stress induced by 2,4-Hx.     

Chronic toxicology and carcinogenesis studies of Telone II by gavage in Fischer-344 rats and B6C3F1 mice

Telone II (technical grade, 1,3-dichloropropene), a soil fumigant, was evaluated in chronic toxicology/carcinogenicity studies using Fischer-344 (F344) rats and B6C3F1 mice of both sexes. Doses administered were 0, 25, or 50 mg/kg to rats and 0, 50, or 100 mg/kg to mice. Telone II was given in corn oil by gavage 3 times per week for 104 wk. Ancillary studies were conducted to determine time-related effects, in which dose groups containing 5 male and 5 females rats were killed after receiving Telone II for 9, 16, 21, 24, or 27 mo. The primary organs affected were the forestomach (rats and mice), urinary bladder (mice), lung (mice), and liver (rats). Compound-related non-neoplastic lesions included basal-cell or epithelial hyperplasia of the forestomach (rats and mice), epithelial hyperplasia of the urinary bladder (mice), and hydronephrosis (mice). Neoplastic lesions associated with administration of Telone II included squamous-cell papillomas of the forestomach (male and female rats, female mice), squamous-cell carcinomas of the forestomach (Male rats, female mice), transitional-cell carcinomas of the urinary bladder (female mice), alveolar/bronchiolar adenomas (female mice), and neoplastic nodules of the liver (male rats). Although cis- and trans-1,3-dichloropropene are the principal components of Telone II, the presence of 1% epichlorohydrin, a direct-acting mutagen and carcinogen added as stabilizer, may have influenced the development of forestomach lesions. The results of the ancillary studies supported the findings of the carcinogenesis studies and demonstrated the time-dependent development of lesions in the forestomach (basal-cell hyperplasia and squamous-cell papilloma). Under the conditions of these gavage studies, Telone II was shown to be carcinogenic in male and female F344 rats and female B6C3F1 mice. Although the study in male B6C3F1 mice was considered inadequate because of the low survival resulting from suppurative inflammation of the heart (myocarditis) in the control group, there was some indication of Telone II-related increases of transitional-cell carcinomas of the urinary bladder, squamous-cell papillomas of the forestomach, and alveolar/bronchiolar adenomas and carcinomas of the lung.     

NTP toxicology and carcinogensis Studies of 2,4-hexadienal (89% trans,trans isomer, CAS No. 142-83-6; 11% cis,trans isomer) (Gavage Studies)

2,4-Hexadienal, a colorless to yellow liquid with a pungent "green" or citrus odor, is used as a food additive for flavor enhancement, as a fragrance agent, as a starting material or intermediate in synthetic reactions in the chemical and pharmaceutical industries, as a fumigant, and as a corrosion inhibitor for steel. 2,4-Hexadienal was nominated for study by the National Cancer Institute because of the potential for carcinogenicity based on its alpha,beta-unsaturated aldehyde structure and the potential link between exposure to lipid peroxidation products in the diet and human malignancies. The commercial product is a mixture containing chiefly trans,trans-2,4-hexadienal in equilibrium with cis,trans-2,4-hexadienal. Male and female F344/N rats and B6C3F1 mice received 2,4-hexadienal (89% trans,trans; 11% cis,trans) in corn oil by gavage for 16 days, 14 weeks, or 2 years. Tissues and plasma from dosed rats were examined for malondialdehyde and glutathione concentrations, and DNA adducts were characterized in liver and forestomach samples from dosed rats and mice. Genetic toxicology studies were conducted in Salmonella typhimurium, rat and mouse bone marrow cells, and mouse peripheral blood erythrocytes. 16-DAY STUDY IN RATS: Groups of five male and five female rats were administered 0, 3, 9, 27, 80, or 240 mg 2,4-hexadienal/kg body weight in corn oil by gavage, 5 days per week, for 16 days. Three male and three female 240 mg/kg rats died before the end of the study. Mean body weight gains of 240 mg/kg rats were significantly less than those of the vehicle controls. Clinical findings included diarrhea, ataxia, lethargy, and nasal/eye discharge in males, and lethargy, paleness, and abnormal breathing in females in the 240 mg/kg groups. Liver weights of 240 mg/kg females were significantly greater than those of the vehicle controls. Gross and microscopic lesions indicative of forestomach necrosis and ulceration were present in most 240 mg/kg rats, and forestomach epithelial hyperplasia was microscopically evident in most 80 mg/kg rats. 16-DAY STUDY IN MICE: Groups of five male and five female mice were administered 2,4-hexadienal in corn oil by gavage at doses of 0, 3, 9, 27, 80, or 240 mg/kg, 5 days per week, for 16 days. Chemical-related deaths occurred in one male and one female in the 240 mg/kg groups. Female mice in the 240 mg/kg group lost weight during the study. Gross and microscopic lesions indicative of forestomach necrosis and ulceration were present in all 240 mg/kg mice, and forestomach epithelial hyperplasia and hyperkeratosis were microscopically evident in 80 mg/kg mice. 14-WEEK STUDY IN RATS: Groups of 10 male and 10 female rats were administered 2,4-hexadienal in corn oil by gavage at doses of 0, 7.5, 15, 30, 60, or 120 mg/kg, 5 days per week, for 14 weeks. All rats survived to the end of the study. Mean body weights of 30, 60, and 120 mg/kg males were significantly less than those of the vehicle controls. The only clinical finding attributed to 2,4-hexadienal administration was hypersalivation in 30 and 120 mg/kg males and females. The incidences of forestomach hyperplasia and nasal olfactory atrophy or necrosis were significantly increased in 120 mg/kg rats. Nasal lesions occurred in most 120 mg/kg male rats. 14-WEEK STUDY IN MICE: Groups of 10 male and 10 female mice were administered 2,4-hexadienal in corn oil by gavage at doses of 0, 7.5, 15, 30, 60, or 120 mg/kg, 5 days per week, for 14 weeks. No deaths were attributed to administration of 2,4-hexadienal. Mean body weights of males and females were similar to those of the vehicle controls throughout the study. Clinical findings included salivation and anal wetness in males and females. Kidney weights of 60 and 120 mg/kg males and liver weights of 60 mg/kg males and females were significantly greater than those of the vehicle controls. The incidences of forestomach hyperplasia and/or nasal olfactory atrophy or necrosis were significantly increased in 120 mg/kg mice. 2-YEAR STUDY IN RATS: Groups of 50 male and 50 female rats were administered 2,4-hexministered 2,4-hexadienal in corn oil by gavage at doses of 0, 22.5, 45, or 90 mg/kg, 5 days per week, for up to 105 weeks. Survival of all dosed groups of rats was similar to that of the vehicle control groups. The mean body weights of 90 mg/kg males were generally less than those of the vehicle controls throughout the study. The incidences of squamous cell papilloma of the forestomach occurred with positive trends in male and female rats. This neoplasm was found in 58% of males and 34% of females in the 90 mg/kg groups. In the forestomach of male rats, papilloma multiplicity was increased in the 90 mg/kg group, and squamous cell carcinomas were found in one 45 mg/kg male and two 90 mg/kg males. Epithelial hyperplasia of the forestomach occurred in most 45 and 90 mg/kg rats. 2-YEAR STUDY IN MICE: Groups of 50 male and 50 female mice were administered 2,4-hexadienal in corn oil by gavage at doses of 0, 30, 60, or 120 mg/kg, 5 days per week, for up to 105 weeks. Survival of dosed mice was similar to that of the vehicle controls. The mean body weights of all dosed groups were generally similar to those of the vehicle controls throughout the study. The incidences of squamous cell papilloma of the forestomach occurred with positive trends in male and female mice; squamous cell carcinomas were present in 120 mg/kg males and females. Epithelial hyperplasia of the forestomach occurred in many 120 mg/kg mice. Two 120 mg/kg males had uncommon squamous cell carcinoma of the oral cavity (tongue). GENETIC TOXICOLOGY: 2,4-Hexadienal was mutagenic in S. typhimurium strain TA100 with and without induced hamster or rat liver enzymes; no mutagenic activity was detected with strains TA1535 or TA98, with or without S9. Results of bone marrow tests in male rats and male mice given intraperitoneal injections of 2,4-hexadienal showed a small increase in the induction of micronucleated erythrocytes. However, neither test was repeated, and the test results were judged to be inconclusive. Results of peripheral blood micronucleus tests in male and female mice treated with 2,4-hexadienal by gavage for 14 weeks were negative. CONCLUSIONS: Under the conditions of these 2-year gavage studies, there was clear evidence of carcinogenic activity* of 2,4-hexadienal in male and female F344/N rats and male and female B6C3F1 mice based on increased incidences of squamous cell neoplasms of the forestomach. The occurrence of squamous cell carcinoma of the oral cavity (tongue) in male B6C3F1 mice may have been related to the administration of 2,4-hexadienal. Hyperplasia of the forestomach in male and female rats and mice was associated with administration of 2,4-hexadienal. Synonyms: Hexa-2,4-dienal; 2,4-hexadienal; 2,4-hexadien-1-al; 2,4-Hx; 1,3-pentadiene-1-carboxaldehyde; 2-propylene acrolein; sorbaldehyde; sorbic aldehyde     

Toxicology and carcinogenesis studies of bis(2-chloroethoxy)methane (CAS No. 111-91-1) in F344/N rats and B6C3F1 mice (dermal studies)

Bis(2-chloroethoxy)methane is used as a solvent and the starting agent in the production of fungicides and polysulfide polymers. Bis(2-chloroethoxy)methane was nominated for study by the National Institute of Environmental Health Sciences because of its widespread use as a starting material to produce polysulfide elastomers, and because there were no 2-year carcinogenicity studies reported in the literature. Male and female F344/N rats and B6C3F1 mice received dermal applications of bis(2-chloroethoxy)-methane in ethanol (greater than 98% pure) for 2 weeks, 3 months, or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium and Escherichia coli, rat bone marrow cells, and mouse peripheral blood erythrocytes. 2-WEEK STUDY IN RATS: Groups of five male and five female rats were dermally administered 0, 12.5, 25, 50, 100, or 200 mg bis(2-chloroethoxy)methane/kg body weight in ethanol, 5 days per week for 16 days. All rats survived to the end of the study. Mean body weights of dosed rats were similar to those of the vehicle control groups. There were no histopathologic lesions related to bis(2-chloroethoxy)methane administration. 2-WEEK STUDY IN MICE: Groups of five male and five female mice were dermally administered 0, 12.5, 25, 50, 100, or 200 mg bis(2-chloroethoxy)methane/kg body weight in ethanol, 5 days per week for 17 days. All mice survived to the end of the study. Mean body weights of dosed mice were similar to those of the vehicle control groups. There were no histopathologic lesions related to bis(2-chloroethoxy)methane administration. 3-MONTH STUDY IN RATS: Groups of 10 male and 10 female rats were dermally administered 0, 50, 100, 200, 400, or 600 mg bis(2-chloroethoxy)methane/kg body weight in ethanol, 5 days per week for 14 weeks. Additional clinical pathology groups of 10 male and 10 female rats were administered the same doses for 23 days. All core study 600 mg/kg males and females and two 400 mg/kg females died before the end of the study. The cause of death was considered to be related to the cardiotoxic effect of bis(2-chloroethoxy)methane. There were no significant differences between final mean body weights of dosed rats and those of the vehicle control groups; the mean body weight gain of 400 mg/kg males was significantly less than that of the vehicle controls. Clinical findings included prostration and ataxia in 600 mg/kg rats during the first week of the study and nasal/eye discharge, lethargy, ataxia, and abnormal breathing in 400 and 600 mg/kg females beginning week 5. An enlarged heart was noted in one 100 mg/kg female rat. Relative kidney weights of 100, 200, and 400 mg/kg males were significantly greater than that of the vehicle control group. Increased incidences and severities of myofiber cytoplasmic vacuolization and interstitial mononuclear cell infiltration in the heart occurred in 400 and 600 mg/kg male and female rats and in 200 mg/kg females. Increased incidences and severities of myofiber necrosis occurred in 600 mg/kg males and females; one female each in the 200 and 400 mg/kg groups also had this lesion. Three 600 mg/kg males had atrial thrombosis. 3-MONTH STUDY IN MICE: Groups of 10 male and 10 female mice were dermally administered 0, 50, 100, 200, 400, or 600 mg bis(2-chloroethoxy)methane/kg body weight in ethanol, 5 days per week for 14 weeks. Except for three 600 mg/kg females, all mice survived to the end of the study. Mean body weights of dosed and vehicle control mice were similar. One 600 mg/kg female that died early exhibited lethargy, abnormal breathing, and tremors, and one animal had clonic seizures. One 600 mg/kg female that died early had focal erosion of the glandular stomach and a focus in the duodenum found to consist of acute suppurative inflammation and thrombosis. Absolute and relative kidney weights of 400 and 600 mg/kg males and 600 mg/kg females were significantly greater than those of the vehicle control groups. Absolute liver weights of 400 and 600 mg/kg females were also significantly increased. Significantly increased incidences of myofiber cytoplasmic vacuolization occurred in 400 and 600 mg/kg females. 2-YEAR STUDY IN RATS: Groups of 50 male and 50 female rats were dermally administered 0, 75, 150, or 300 mg bis(2-chloroethoxy)methane/kg body weight in ethanol, 5 days per week for 105 weeks. Survival of all dosed groups of rats was generally similar to that of the vehicle controls. Mean body weights of dosed rats were similar to those of the vehicle controls throughout the study. Clinical findings in 300 mg/kg females that died during the first year of the study included abnormal breathing, lethargy, thinness, nasal discharge, and ataxia. Significantly increased incidences of degeneration of the olfactory epithelium in the nose occurred in all dosed groups of males and in 150 and 300 mg/kg females. The incidences of inflammation of the forestomach were significantly increased in 150 and 300 mg/kg males, and the incidence of ulcers was significantly increased in 300 mg/kg males. Increased incidences of cystic degeneration of the liver occurred in 150 and 300 mg/kg male rats; the incidence was significantly increased in the 300 mg/kg group. 2-YEAR STUDY IN MICE: Groups of 50 male mice were dermally administered 0, 150, 300, or 600 mg bis(2-chloroethoxy)methane/kg body weight in ethanol, 5 days per week for 105 weeks. Groups of 50 female mice were dermally administered 0, 100, 200, or 400 mg/kg in ethanol, 5 days per week for 104 weeks. Survival of 600 mg/kg male mice was significantly less than that of the vehicle control group. Mean body weights of dosed mice were generally similar to those of the vehicle controls throughout the study. Clinical findings observed in 600 mg/kg male mice that died during the first year of the study included lethargy and thinness. Myocardial heart changes were recorded according to the characteristic lesions of cardiomyopathy syndrome (necrosis, mononuclear cell infiltration, myocardial cell vacuolization, and interstitial fibrosis) separately, and in addition, where appropriate, they were also categorized as cardiomyopathy. Increased incidences of cardiomyopathy and mononuclear cell infiltration occurred in 600 mg/kg males and 400 mg/kg females; the incidences were significantly increased in 600 mg/kg males compared to the vehicle controls. Significantly increased incidences of cardiomyocyte vacuolization and interstitial fibrosis occurred in 600 mg/kg males. A few early deaths in the 600 mg/kg males were considered to be due, at least in part and probably exclusively, to bis(2-chloroethoxy)methane-induced cardiotoxicity. The incidence of ulceration of the forestomach was significantly increased in 600 mg/kg males. Significantly increased incidences of dermal inflammation and fibrosis and epidermal hyperplasia at the site of application occurred in 600 mg/kg male mice. GENETIC TOXICOLOGY: Bis(2-chloroethoxy)methane was mutagenic in S. typhimurium strains TA100 and TA1535 in the presence of exogenous metabolic activation enzymes (S9) in one study; results from a second bacterial mutagenicity test were judged to be equivocal based on responses observed in TA100 and in E. coli strain WP2 uvrA/pKM101 in the presence of S9. No mutagenicity was observed in other tester strains or in the absence of S9. Bis(2-chloroethoxy)methane did not increase the frequency of micronucleated reticulocytes in bone marrow of male F344/N rats following three daily treatments by gavage or micronucleated erythrocytes in peripheral blood of male or female mice after 3 months of dermal exposure. CONCLUSIONS: Under the conditions of these 2-year dermal studies, there was no evidence of carcinogenic activity of bis(2-chloroethoxy)methane in male or female F344/N rats administered 75, 150, or 300 mg/kg. There was no evidence of carcinogenic activity of bis(2-chloroethoxy)methane in male B6C3F1 mice administered 150, 300, or 600 mg/kg or in female B6C3F1 mice administered 100, 200, or 400 mg/kg. The administration of bis(2-chloroethoxy)methane for 2 years resulted in increased incidences of nonneoplastic lesions in the nose of male and female rats, the forestomach of male rats, the heart of male and female mice, and the forestomach and skin of male mice.     

Encephalopathy in rats and nephropathy in rats and mice after subchronic oral exposure to benzaldehyde

Male and female Fischer 344 rats and B6C3F1 mice were treated daily (5 days/wk) with benzaldehyde by gavage either in 12 doses of 0 (vehicle control), 100 (rats only), 200, 400, 800, 1600 or (for mice only) 3200 mg/kg body weight/day (followed by 2 days' observation without treatment), or for 90 days in doses of 0, 50, 100, 200, 400 or 800 mg/kg/day (rats) or 0, 75, 150, 300, 600 or 1200 mg/kg/day (mice). In the acute studies, benzaldehyde induced deaths and decreased body-weight gain in both sexes of rats given 800 or 1600 mg/kg/day and caused deaths in both sexes of mice given 1600 or 3200 mg/kg/day. In the 90-day studies, deaths occurred in both sexes of rats on 800 mg/kg/day and in male mice on 1200 mg/kg/day. Body-weight gain was depressed in male rats on 800 mg/kg/day, in male mice on 600 mg/kg/day and in female mice on 1200 mg/kg/day. Necrotic and degenerative lesions were seen in the cerebellar and hippocampal regions of the brain in both sexes of rats given 800 mg/kg/day, but not in mice. Renal tubular necrosis occurred in male and female rats on 800 mg/kg/day and in male mice on 1200 mg/kg/day. Mild epithelial hyperplasia or hyperkeratosis of the forestomach was seen in male and female rats on 800 mg/kg/day. In this limited study, the no-observed-toxic-effect doses of benzaldehyde administered by gavage were 400 mg/kg/day in male and female rats, 300 mg/kg/day in male mice and 600-1200 mg/kg/day in female mice.     

Toxicity and Carcinogenicity of 2,3-Dibromo-1-propanol in F344/N Rats and B6C3F1 Mice

2,3-Dibromo-1-propanol is a metabolite of the flame retardanttris(2,3-dibromopropyl) phosphate, previously shown to be amutagen and carcinogen in experimental animals. Toxicology andcarcinogenesis studies of 2,3-dibromo-1-propanol were conductedby applying the chemical in 95% ethanol to the interscapularskin of male and female F344/N rats and B6C3F₁ mice 5 days aweek for 13 weeks in the prechronic study and 48–55 weeks(rats) or 36–42 weeks (mice) in the carcinogenicity study.In the 13-week study, 10 rats and 10 mice of each sex receiveddoses of 0, 44, 88, 177, 375, or 750 mg/kg. Deaths associatedwith chemical application occurred only in the high-dose (750mg/kg) male mice. Chemical-related lesions were seen in thekidney of male rats, liver of female rats, and liver and lungof both sexes of mice. Based on the toxicity observed in the13-week study, 50 rats of each sex received doses of 0, 188,or 375 mg/kg and 50 mice of each sex received 0, 88, or 177mg/kg in the carcinogenicity study. The planned 2-year studywas terminated early because of reduced survival of rats relatedto chemical-induced neoplasia and because of the appearanceof antibodies to lymphocytic choriomeningitis virus in sentinelmice. Nearly all dosed rats had malignant neoplasms at one ormore sites, while only one control male and one control femalehad malignant neoplasms. In rats, neoplasms induced by 2,3-dibromo-1-propanoloccurred in the skin, nasal mucosa, Zymbal's gland, oral mucosa,esophagus, forestomach, intestines, liver, kidney, mammary gland(females), clitoral gland (females), spleen (males), and mesothelium(males). In mice, chemical-induced neoplasms occurred in theskin, forestomach, liver (males), and lung (males).     

Acrylonitrile is a multisite carcinogen in male and female B6C3F1 mice.

Acrylonitrile is a heavily produced unsaturated nitrile, which is used in the production of synthetic fibers, plastics, resins, and rubber. Acrylonitrile is a multisite carcinogen in rats after exposure via gavage, drinking water, or inhalation. No carcinogenicity studies of acrylonitrile in a second animal species were available. The current studies were designed to assess the carcinogenicity of acrylonitrile in B6C3F1 mice of both sexes. Acrylonitrile was administered by gavage at 0, 2.5, 10, or 20 mg/kg/day, 5 days per week, for 2 years. Urinary thiocyanate and N-acetyl-S-(2-cyanoethyl)-L-cysteine were measured as markers of exposure to acrylonitrile. In general, there were dose-related increases in urinary thiocyanate and N-acetyl-S-(2-cyanoethyl)-L-cysteine concentrations in all dosed groups of mice and at all time points. Survival was significantly (p < 0.001) reduced in the top dose (20 mg/kg) group of male and female mice relative to controls. The incidence of forestomach papillomas and carcinomas was increased in mice of both sexes in association with an increase in forestomach epithelial hyperplasia. The incidence of Harderian gland adenomas and carcinomas was also markedly increased in the acrylonitrile-dosed groups. In female mice, the incidence of benign or malignant granulosa cell tumors (combined) in the ovary in the 10 mg/kg dose group was greater than that in the vehicle control group, but because of a lack of dose response, this was considered an equivocal finding. In addition, the incidences of atrophy and cysts in the ovary of the 10 and 20 mg/kg dose groups were significantly increased. The incidences of alveolar/bronchiolar adenoma or carcinoma (combined) were significantly increased in female mice treated with acrylonitrile at 10 mg/kg/day for 2 years. This was also considered an equivocal result. In conclusion, these studies demonstrated that acrylonitrile causes multiple carcinogenic effects after gavage administration to male and female B6C3F1 mice for 2 years.     

Toxicity and carcinogenicity of hydroquinone in F344/N rats and B6C3F1 mice.

Toxicology and carcinogenesis studies were conducted by administering hydroquinone (more than 99% pure) by gavage to groups of F344/N rats and B6C3F1 mice of each sex for 14 days, 13 wk or 2 yr. 14-day studies were conducted by administering hydroquinone in corn oil to rats at doses ranging from 63 to 1000 mg/kg body weight and to mice at doses ranging from 31 to 500 mg/kg, 5 days/wk. In the 13-wk studies, doses for rats and mice ranged from 25 to 400 mg/kg. At those doses showing some indication of toxicity in the 14-day and 13-wk studies, the central nervous system, forestomach and liver were identified as target organs in both species and renal toxicity was observed in rats. Based on these results, 2-yr studies were conducted by administering 0, 25 or 50 mg hydroquinone/kg in deionized water by gavage to groups of 65 rats of each sex, 5 days/wk. Groups of 65 mice of each sex were given 0, 50 or 100 mg/kg on the same schedule. 10 rats and 10 mice from each group were killed and evaluated after 15 months. Mean body weights of high-dose male rats and high-dose mice were approx. 5-14% lower than those of controls during the second half of the study. No differences in survival were observed between dosed and control groups of rats or mice. Nearly all male rats and most female rats in all vehicle control and exposed groups had nephropathy, which was judged to be more severe in high-dose male rats. Hyperplasia of the renal pelvic transitional epithelium and renal cortical cysts were increased in male rats. Tubular cell hyperplasia of the kidney was seen in two high-dose male rats, and renal tubular adenomas were seen in 4/55 low-dose and 8/55 high-dose male rats; none was seen in vehicle controls or in female rats. Mononuclear cell leukaemia in female rats occurred with increased incidences in the dosed groups (vehicle control, 9/55; low dose, 15/55; high dose, 22/55). Compound-related lesions observed in the liver of high-dose male mice included anisokaryosis, syncytial alteration and basophilic foci. The incidences of hepatocellular neoplasms, primarily adenomas, were increased in dosed female mice (3/55; 16/55; 13/55). Follicular cell hyperplasia of the thyroid gland was increased in dosed mice.(ABSTRACT TRUNCATED AT 400 WORDS)     

Forestomach neoplasms in Fischer F344/N rats and B6C3F1 mice exposed to diglycidyl resorcinol ether--an epoxy resin

Repeated dose (14 days), subchronic (13 wk) and chronic (2 yr) studies were carried out in succession to evaluate the toxic and carcinogenic effects of diglycidyl resorcinol ether (DGRE), a liquid spray epoxy resin, in F344/N rats and B6C3F1 mice. DGRE in corn oil was administered by gavage for 14 consecutive days in the repeated dose study and 5 days/wk in the subchronic and chronic studies. The mortality rate was increased in rats and mice in the repeated dose and subchronic studies. Hyperkeratosis, basal cell hyperplasia and squamous cell papillomas of the forestomach were observed in a few treated rats and mice in the subchronic study. Based on the results of the subchronic study, F344/N rats and B6CF1 mice (50 males and 50 females/species/dose) were administered DGRE (rats--0, 12, 25 and 50 mg/kg body weight, mice--0, 50 and 100 mg/kg body weight) in corn oil by gavage 5 days/wk for 103 wk. The incidence of neoplastic and non-neoplastic changes of the forestomach was increased in rats and mice in the chronic study. Under the conditions of the study, DGRE is considered to be carcinogenic to F344/N rats and B6C3F1 mice.     

Comparative toxicity of ethylene dichloride in F344/N, Sprague-Dawley and Osborne-Mendel rats

Studies were conducted to compare the toxicity of ethylene dichloride (EDC) in F344/N rats, Sprague-Dawley rats, and Osborne-Mendel rats. Ten rats/sex/group were exposed to EDC in drinking-water at 0, 500, 1000, 2000, 4000 and 8000 ppm for 13 wk. The highest concentration was limited by the maximum solubility of EDC in water (about 9000 ppm). In addition, F344/N rats (10/sex/group) were administered EDC in corn oil by gavage to compare toxicity resulting from bolus administration with that of continuous exposure in drinking-water. Gavage doses of EDC were within the range of total daily doses (in mg/kg body weight/day) resulting from exposure in drinking-water. EDC administered by gavage resulted in greater toxicity to F344/N rats than did administration of similar doses in drinking-water. All males receiving 240 and 480 mg/kg body weight and 9/10 females receiving 300 mg/kg body weight by gavage died before the end of the study. Necrosis of the cerebellum was observed in the brains of 3 males receiving 240 mg/kg body weight and 3 females receiving 300 mg/kg body weight. Hyperplasia and inflammation of the forestomach mucosa were observed in 8 male and 3 female rats that died or were killed in moribund condition. EDC caused minimal toxicity to F344/N, Sprague-Dawley and Osborne-Mendel rats at the drinking-water concentrations used in these studies; only female F344/N rats had EDC-related renal lesions. Based on mortality and EDC-related lesions, the no-effect levels for EDC administered by gavage to F344/N rats were 120 mg/kg body weight for males and 150 mg/kg body weight for females.     

Toxicology and carcinogenesis studies of ginseng (CAS No. 50647-08-0) in F344/N rats and B6C3F1 mice (gavage studies)

CHEMICAL AND PHYSICAL PROPERTIES: Ginseng is a perennial aromatic herb widely used in herbal remedies, dietary supplements, cosmetics, and as a food additive. Ginseng was nominated for study by the National Cancer Institute based on significant human exposure through the uses described above and the lack of information on its toxicity. Male and female F344/N rats and B6C3F1 mice were administered extracts of ginseng root by gavage for 2 weeks, 3 months, or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium, Escherichia coli, and mouse peripheral blood erythrocytes. 2-WEEK STUDY IN RATS: Groups of five male and five female rats were administered ginseng in 0.5% aqueous methylcellulose by gavage at doses of 0, 125, 250, 500, 1,000, or 2,000 mg/kg, 5 days per week for 16 days. All rats survived to the end of the study. Mean body weight gain of 2,000 mg/kg males was significantly greater than that of the vehicle controls. There were no chemical-related gross or microscopic findings attributed to the administration of ginseng. 2-WEEK STUDY IN MICE: Groups of five male and five female mice were administered ginseng in 0.5% aqueous methylcellulose by gavage at doses of 0, 125, 250, 500, 1,000, or 2,000 mg/kg, 5 days per week for 17 days. All mice survived to the end of the study. The final mean body weight of 1,000 mg/kg males was significantly less than that of the vehicle controls. There were no significant chemical-related gross or histopathologic changes in dosed mice. 3-MONTH STUDY IN RATS: Groups of 10 male and 10 female rats were administered ginseng in sterile water by gavage at doses of 0, 1,000, 2,000, 3,000, 4,000, or 5,000 mg/kg, 5 days per week for 14 weeks. All rats survived to the end of the study. Mean body weights of all dosed groups were similar to those of the vehicle control groups. No lesions that were observed by gross or histopathologic examination were attributed to the administration of ginseng. 3-MONTH STUDY IN MICE: Groups of 10 male and 10 female mice were administered ginseng in sterile water by gavage at doses of 0, 1,000, 2,000, 3,000, 4,000, or 5,000 mg/kg, 5 days per week for 14 weeks. All mice survived to the end of the study. Mean body weights of all dosed groups were similar to those of the vehicle control groups. Although sporadic incidences of lesions were observed in the vehicle control and 5,000 mg/kg groups, there were no chemical-related gross or microscopic findings in dosed mice. 2-YEAR STUDY IN RATS: Groups of 50 male and 50 female rats were administered ginseng in sterile water by gavage at doses of 0, 1,250, 2,500, or 5,000 mg/kg, 5 days per week for 104 to 105 weeks. Survival of 5,000 mg/kg females was significantly less than that of the vehicle controls; however, the deaths were not attributed to the administration of ginseng because no histopathologic findings attributable to ginseng were found. Mean body weights of 5,000 mg/kg females were less than those of the vehicle controls after week 61 of the study, and mean body weights of other dosed groups of rats were similar to those of the vehicle controls throughout the study. No increases in the incidences of neoplasms or nonneoplastic lesions were attributed to the administration of ginseng. The incidence of mammary gland fibroadenoma was significantly decreased in 5,000 mg/kg females. 2-YEAR STUDY IN MICE: Groups of 50 male and 50 female mice were administered ginseng in sterile water by gavage at doses of 0, 1,250, 2,500, or 5,000 mg/kg, 5 days per week for 105 weeks. Survival of dosed groups was similar to that of the vehicle control groups. Mean body weights of dosed mice were similar to those of the vehicle controls. No neoplasms or nonneoplastic lesions were attributed to the administration of ginseng. GENETIC TOXICOLOGY: Ginseng was not mutagenic in either of two independent bacterial mutagenicity assays, each conducted with or without exogenous metabolic activation enzymes. Bacterial strains tested included S. typhimurium strains TA97, TA98, TA100, TA102, TA104, and TA1535, as well as E. coli strain WP2 uvrA/pKM101. No significant increases were seen in the frequencies of micronucleated erythrocytes in the peripheral blood of male or female B6C3F1 mice exposed for 3 months to 1,000 to 5,000 mg/kg ginseng via gavage. CONCLUSIONS: Under the conditions of these 2-year gavage studies, there was no evidence of carcinogenic activity of ginseng in male or female F344/N rats or B6C3F1 mice administered 1,250, 2,500, or 5,000 mg/kg. The incidence of mammary gland fibroadenoma was significantly decreased in 5,000 mg/kg female rats.     

Benzyl acetate carcinogenicity, metabolism, and disposition in Fischer 344 rats and B6C3F1 mice

Carcinogenesis studies of benzyl acetate (a fragrance and flavoring agent) were conducted in F344 rats and B6C3F1 mice. The chemical was given in corn oil by gavage once daily, 5 days/week for 103 weeks, to groups of 50 animals of each sex and species. For rats the doses were 0, 250, and 500 mg/kg body weight and for mice the doses were 0, 500, and 1000 mg/kg. Mean body weights of control and dosed rats and mice were not affected adversely by benzyl acetate. The survival of control and low dose female mice was lower than that of the high dose group. A genital tract infection may have contributed to the reduced survival. No other significant difference in survival was observed for dosed rats or mice. Benzyl acetate was absorbed from the gastrointestinal tract of rats and mice, with approximately 90% of the administered dose recovered as various metabolites in the urine within 24 h. The primary metabolite was hippuric acid, with minor amounts of a mercapturic acid, and one or more unidentified metabolites. This capacity for absorption, metabolism, and disposition was unaffected by the amount or number of doses administered. Under the conditions of these studies, benzyl acetate administration was associated with an increased incidence of acinar cell adenoma of the exocrine pancreas in male F344/N rats. No evidence of carcinogenicity was found for female F344/N rats. For male and female B6C3F1 mice there was evidence of carcinogenicity, in that benzyl acetate caused an increased incidence of hepatocellular neoplasms (particularly adenomas) and squamous cell neoplasms of the forestomach.     

Toxicology and carcinogenesis studies of methyl trans-styryl ketone (CAS NO 1896-62-4) in F344/N rats and B6C3F1 mice (feed and dermal studies)

Methyl trans-styryl ketone is used as a synthetic flavoring agent and a fragrance additive in food and personal care products. Methyl trans-styryl ketone was nominated for study by the National Cancer Institute due to widespread human exposure as a flavoring and fragrance additive, positive results in the Ames/Salmonella assay and the mouse lymphoma L5178Y/tk+/- assay, and as a representative of the α,β-unsaturated ketone chemical class. Male and female F344/N rats and B6C3F1 mice received methyl trans-styryl ketone (98.6% pure) in feed for 3 months and dermally for 3 months or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium, Escherichia coli, and mouse peripheral blood erythrocytes. Two-year studies were conducted to provide data for assessment of possible toxicity due to exposure to methyl trans-styryl ketone. The dermal route was chosen since this is the route for highest human exposure and due to studies demonstrating systemic exposure following dermal application to methyl trans-styryl ketone. 3-MONTH FEED STUDY IN RATS Groups of 10 male and 10 female rats were fed diets containing 0%, 0.025%, 0.05%, 0.1%, 0.2%, or 0.4% methyl trans-styryl ketone (equivalent to average daily doses of approximately 18, 36, 72, 145, or 290 mg methyl trans-styryl ketone/kg body weight to males and 19, 38, 77, 150, or 300 mg/kg to females) for 14 weeks. Groups of 10 male and 10 female clinical pathology rats were fed the same concentrations for 24 days. All core study rats survived to the end of the study. Final mean body weights of males and females receiving 0.4% and mean body weight gains of males receiving 0.4% were significantly less than those of the controls. Feed consumption by exposed groups was similar to that by the controls. Clinical findings included diarrhea and hyperactivity in males and females. Results of sperm motility and vaginal cytology evaluations indicated methyl trans-styryl ketone is unlikely to be a reproductive toxicant in male rats; however, it exhibits potential for reproductive toxicity in female rats based upon an increased probability of extended diestrus at the highest exposure concentration. In all exposed groups of males, there were treatment-related increased incidences of goblet cell hyperplasia of the respiratory epithelium of the nose and nephropathy of the kidney. In females, there was an increased incidence of goblet cell hyperplasia of the respiratory epithelium of the nose in the group receiving 0.4%. 3-MONTH FEED STUDY IN MICE: Groups of 10 male and 10 female mice were fed diets containing 0%, 0.025%, 0.05%, 0.1%, 0.2%, or 0.4% methyl trans-styryl ketone (equivalent to average daily doses of approximately 55, 110, 220, 400, or 750 mg/kg to males and 50, 100, 200, 350, or 600 mg/kg to females) for 14 weeks. One male receiving 0.2% and one control female died before the end of the study. Mean body weights of males and females receiving 0.4% were significantly less than those of the controls. Feed consumption by exposed groups was similar to that by the controls. Hyperactivity in both sexes was the only clinical finding. Results of sperm motility and vaginal cytology evaluations indicated methyl trans-styryl ketone is unlikely to be a reproductive toxicant in male mice; however, it exhibits potential for reproductive toxicity in female mice based upon an increased probability of extended diestrus at the lowest and the highest exposure concentrations. There were significantly increased incidences of olfactory epithelial atrophy of the nose in males and females receiving 0.4%. 3-MONTH DERMAL STUDY IN RATS: Groups of 10 male and 10 female rats were dermally administered 0, 22, 44, 87.5, 175, or 350 mg methyl trans-styryl ketone/kg body weight in 95% ethanol, 5 days per week for 14 weeks. Groups of 10 male and 10 female clinical pathology rats were administered the same doses for 23 days. All rats survived to the end of the study. Mean body weights of 175 and 350 mg/kg males were significantly less than that of the vehicle controls. Clinical findings in groups administered 175 or 350 mg/kg included dermal irritation, thickened skin, and ulceration at the site of application. Results of sperm motility and vaginal cytology evaluations indicated methyl trans-styryl ketone is unlikely to be a reproductive toxicant in male or female rats at the doses used in this study. Histologically, there were significantly increased incidences of epidermal hyperplasia, hyperkeratosis, chronic active inflammation, epidermal necrosis, and sebaceous gland hypertrophy in the skin at the site of application in males and/or females. There were significantly increased incidences of goblet cell hyperplasia of the nose in 350 mg/kg males and 22, 175, and 350 mg/kg females. 3-MONTH DERMAL STUDY IN MICE Groups of 10 male and 10 female mice were dermally administered 0, 87.5, 175, 350, 700, or 1,400 mg methyl trans-styryl ketone/kg body weight in 95% ethanol, 5 days per week for 13 weeks. All mice in the 700 and 1,400 mg/kg groups were sacrificed moribund before the end of the study. The final mean body weights of surviving groups of dosed males and females were similar to those of the vehicle controls; however, the mean body weight gains of the 175 mg/kg groups were significantly less than those of the vehicle controls. Clinical findings at the site of application included dermal irritation in 350 mg/kg males and crust formation in all 700 and 1,400 mg/kg mice except one female. Results of sperm motility and vaginal cytology evaluations indicated methyl trans-styryl ketone is unlikely to be a reproductive toxicant in male or female mice at the doses used in this study. There were treatment-related increased incidences of epidermal hyperplasia, hyperkeratosis, chronic active inflammation, epidermal necrosis, sebaceous gland hypertrophy, and hair follicle hyperplasia in the skin at the site of application in males and females. There were increased incidences of olfactory epithelial atrophy of the nose in groups of males and females administered 350 mg/kg or greater. 2-YEAR DERMAL STUDY IN RATS: Groups of 50 male and 50 female rats were dermally administered 0, 10, 30, or 90 mg methyl trans-styryl ketone/kg body weight in 95% ethanol, 5 days per week for 105 weeks. Survival of all dosed groups was similar to that of the vehicle controls. Mean body weights of dosed groups were within 10% of those of the vehicle control groups throughout the study. In the skin at the site of application, there were increased incidences of epidermal hyperplasia and hyperkeratosis in males and females administered 30 or 90 mg/kg. 2-YEAR DERMAL STUDY IN MICE: Groups of 50 male and 50 female mice were dermally administered 0, 10, 30, or 90 mg methyl trans-styryl ketone/kg body weight in 95% ethanol, 5 days per week for 105 weeks. Survival of all dosed groups was similar to that of the vehicle controls. Mean body weights of dosed groups were within 10% of those of the vehicle control groups throughout the study. In the skin at the site of application in males and females, there were treatment-related increased incidences of epidermal hyperplasia, hyperkeratosis, chronic inflammation, and melanocyte hyperplasia. GENETIC TOXICOLOGY: Methyl trans-styryl ketone was mutagenic in Salmonella typhimurium strain TA100 when testing was conducted in the presence of rat liver microsomes (S9). No mutagenic activity was seen with methyl trans-styryl ketone in strain TA98 with or without S9 or in Escherichia coli strain WP2 uvrA/pKM101 in the absence of S9. With S9, inconsistent responses were seen in the E. coli tester strain. No increases in the frequencies of micronucleated normochromatic erythrocytes were seen in peripheral blood samples from male or female mice administered methyl trans-styryl ketone for 3 months via dosed feed or dermal application. CONCLUSIONS: Under the conditions of these 2-year dermal studies, there was no evidence of carcinogenic activity of methyl trans-styryl ketone in male or female F344/N rats or in male or female B6C3F1 mice administered 10, 30, or 90 mg/kg. Administration of methyl trans-styryl ketone resulted in nonneoplastic lesions of the skin at the site of application in male and female rats and mice. Synonyms: Acetocinnamone; benzalacetone; benzylideneacetone; methyl 2-phenylvinyl ketone; methyl styryl ketone; methyl β-styryl ketone; MSK; 4-phenyl-3-butene-2-one; 4-phenylbutenone; 2-phenylvinyl methyl ketone; styryl methyl ketone Systematic name: (3E)-4-Phenylbut-3-en-2-one.     

Acute and subchronic toxicity studies on Sel-Plex, a standardized, registered high-selenium yeast

Selenium has been recognized as an essential nutrient for human health; however, its bioavailability is primarily dependent upon the type of selenium, elemental versus organic. In geographic areas low in selenium, there is the potential for animals (including humans) to become selenium deficient and this potential deficiency can be remedied by consumption of exogenous selenium, including selenium-enriched yeast (Saccharomyces cerevisiae) that contains high levels of organic selenium (e.g., selenized yeast). The present studies were conducted to investigate potential oral toxicity of a unique selenized yeast preparation (Sel-Plex) when administered to (1) adult female CHS Swiss mice ICo:OFI (IOPS Caw); (2) adult female CHS Sprague-Dawley rats; and (3) adult male and female Sprague-Dawley CD rats. For the 28- and 90-day toxicity studies, (1) adult male and female Sprague-Dawley CRL:CD(R)(SD) IGS BR strain rats and (2) adult male and female 6- to 7-month-old Beagle dogs were used. The LD50 for mice was >or=2000 mg Sel-Plex/kg (>or=4.06 mg Se/kg) and for rats, was greater than >or=2000 mg Sel-Plex/kg (>or=4.06 mg Se/kg). In the two 28-day studies, for rats, the no observed adverse effects level (NOAEL) was 50 mg Sel-Plex/kg/day (0.1 mg Se/kg/day), and for the dogs, the NOAEL was 22.5 mg Sel-Plex/kg/day (0.045 mg Se/kg/day). For the two 90-day studies, for rats the NOAEL for Sel-Plex was 114 mg/kg/day (0.23 mg Se/kg/day), and for dogs, the NOAEL was 30 mg Sel-Plex/kg/day (0.06 mg Se/kg/day): the latter being the NOAEL in the most sensitive species.     

Kidney and Urinary Bladder Lesions in F344/N Rats and B6C3F1 Mice after 13 Weeks of 2,2-Bis(bromomethyl)-1,3-propanediol Administration

Kidney and Urinary Bladder Lesions in F344/N Rats and B6C3F1Mice after 13 Weeks of 2,2-Bis(bromomethyl)-1,3-propanediolAdministration. ELWELL., M. R., DUNNICK, J. K., BROWN, H. R.,AND MONTGOMERY, C. A. (1989). Fundam Appl. Toxicol. 12, 480–490.Thir teen-week toxicity studies of the flame retardant 2,2-bis(bromomethyl)-1,3-propanediol(BMP; dibromoneopentyl glycol; FR-1138; CAS No. 329690-0) wereconducted in male and female F344/N rats and B6C3F1 mice. Thechemical was administered by oral gavage in corn oil 5 daysper week for 13 weeks to rats at doses of 0, 50, 100, 200, 400,and 800 mg/kg and to mice at doses of 0, 25, 50, 100, 200, and400 mg/kg, or in the feed for 13 weeks at concentrations of0, 1250, 2500, 5000, 10,000, and 20,000 ppm for rats and at0, 625, 1250, 2500, 5000, and 10,000 ppm for mice. There wasa dose-related decrease in body weight gain in rats and miceafter chemical administration. Mortality attributed to toxicityof BMP was seen in the gavage study in 2/10 high-dose (800 mg/kg)male rats and 3/10 high-dose (400 mg/kg) male mice; no dose-relatedmortality occurred in the feed study. Minimal degeneration inthe renal papilla was seen in male rats at 800 mg/kg in thegavage study and at doses of 5000 ppm or more in the feed study.This was also present in one female rat at the 20,000 ppm dose.In male mice renal papillary necrosis occurred at 400 mg/kgafter dosing by the gavage route and at 2500, 5000, and 10,000ppm in the dosed-feed study. In female mice papillary necrosisoccurred only at the 10,000 ppm dose in the feed study. Tubularcell regeneration of the renal cortex was also present in miceat the same dose levels at which the papillary necrosis wasobserved. Transitional cell hyperplasia of the urinary bladderwas seen in male rats at 400 and 800 mg/kg and in both sexesof mice at 200 and 400 mg/kg. Hyperplasia of the urinary bladderwas also seen when BMP was administered in the feed at dosesof 20,000 ppm to male rats; at doses of 2500, 5000, and 10,000ppm to male mice; and at doses of 5000 and 10,000 ppm to femalemice. The kidney and urinary bladder are target organs whenBMP is administered by gavage or the dosed-feed route; micewere more sensitive than rats for the development of kidneyand bladder lesions. Male rats and mice were more sensitivethan females for the development of renal papillary degenerationor necrosis.     

Toxicology and carcinogenesis studies of formamide (Cas No. 75-12-7) in F344/N rats and B6C3F1 mice (gavage studies)

Formamide is used as a softener for paper, gums, and animal glues; as an ionizing solvent; and in the manufacture of formic esters and hydrocyanic acid. Formamide was nominated for reproductive and genetic toxicity evaluation by the Environmental Defense Fund and for carcinogenicity evaluation by the National Cancer Institute because of the potential for human exposure associated with its widespread industrial use, the absence of data adequately characterizing its potential for reproductive and genetic toxicity, and the fact that acetamide, a compound structurally related to form-amide, is hepatocarcinogenic in rats when administered in feed. Male and female F344/N rats and B6C3F1 mice were administered formamide (approximately 100% pure) in deionized water by gavage for 2 weeks, 3 months, or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium and Escherichia coli, Drosophila melanogaster, and mouse peripheral blood erythrocytes. 3-MONTH STUDY IN RATS: Groups of 10 male and 10 female rats were administered 0, 10, 20, 40, 80, or 160 mg formamide/kg body weight in deionized water by gavage, 5 days per week for 14 weeks. Additional groups of 10 male and 10 female rats (clinical pathology study) and five male and five female rats (plasma concentration study) were administered the same doses, 5 days per week for up to 14 weeks. All core study rats survived to the end of the study. Mean body weights of females in the 40 mg/kg group and males and females in the 80 and 160 mg/kg groups were significantly less than those of the vehicle controls. On day 23 and at week 14, there was a dose-related increase in the erythron, evidenced by increases in hematocrit values, hemoglobin concentrations, and erythrocyte counts. The incidences of degeneration of the germinal epithelium of the testes and epididymis were significantly increased in 160 mg/kg males. 3-MONTH STUDY IN MICE: Groups of 10 male and 10 female mice were administered 0, 10, 20, 40, 80, or 160 mg formamide/kg body weight in deionized water by gavage, 5 days per week for 14 weeks. Additional groups of five male and five female mice (plasma concentration study) were administered the same doses, 5 days per week for 14 weeks. All mice survived to the end of the study. Final mean body weights of the 80 and 160 mg/kg males and mean body weight gains of 40, 80, and 160 mg/kg males were significantly less than those of the vehicle controls. Dosed females differed significantly from vehicle controls in the relative amount of time spent in the estrous stages. All 160 mg/kg males had abnormal residual bodies in the testes. 2-YEAR STUDY IN RATS: Groups of 50 male and 50 female rats were administered 0, 20, 40, or 80 mg formamide/kg body weight, 5 days per week for 104 to 105 weeks in deionized water by gavage. Survival of all dosed groups of rats was similar to that of the vehicle controls. Mean body weights of 80 mg/kg males were less than those of the vehicle controls throughout most of the study. Mean body weights of 40 and 80 mg/kg females were somewhat less than those of the vehicle controls during the second year of the study. A significant increase in the incidence of bone marrow hyperplasia occurred in 80 mg/kg males. No neoplasms were attributed to exposure to formamide. 2-YEAR STUDY IN MICE: Groups of 50 male and 50 female mice were administered 0, 20, 40, or 80 mg formamide/kg body weight, 5 days per week for 104 to 105 weeks in deionized water by gavage. Survival of all dosed groups of mice was similar to that of the vehicle controls. Mean body weights of 80 mg/kg males and females were generally less than those of the vehicle controls throughout the study; mean body weights of 40 mg/kg females were generally less after week 13 of the study. The incidences of hemangiosarcoma of the liver occurred with a positive trend in males, and the incidences were significantly increased in the 40 and 80 mg/kg groups. The incidence of hepatocellular adenoma or carcinoma (combined) in 80 mg/kg females was significantly increased. The incidences of mineralization of the testicular arteries and testicular tunic were significantly increased in 80 mg/kg males. The incidence of hematopoietic cell proliferation of the spleen was significantly increased in 80 mg/kg males. GENETIC TOXICOLOGY: Formamide gave no evidence for mutagenicity in a series of short-term assays. In three independent Ames assays, formamide was not mutagenic in any of several strains of S. typhimurium tested with and without rat or hamster liver S9 activation enzymes or in E. coli strain WP uvrA pKM101 tested with and without 10% rat liver S9. Negative results were obtained in a test for induction of sex-linked recessive lethal mutations in germ cells of male D. melanogaster treated with formamide either by feeding or injection. Formamide did not induce increases in micronucleated erythrocytes in male or female mice treated by gavage for 3 months. CONCLUSIONS: Under the conditions of these 2-year gavage studies, there was no evidence of carcinogenic activity of form-amide in male or female F344/N rats administered 20, 40, or 80 mg/kg. There was clear evidence of carcinogenic activity of formamide in male B6C3F1 mice based on increased incidences of hemangiosarcoma of the liver. There was equivocal evidence of carcinogenic activity of formamide in female B6C3F1 mice based on increased incidences of hepatocellular adenoma or carcinoma (combined). An increased incidence of bone marrow hyperplasia occurred in male rats. Mineralization of the testicular arteries and tunic and hematopoietic cell proliferation of the spleen in male mice were also associated with administration of formamide.     

Toxicology and carcinogenesis studies of diisopropylcarbodiimide (Cas No. 693-13-0) in F344/N rats and B6C3F1 mice (dermal studies)

Diisopropylcarbodiimide is used as a reagent for peptide syntheses and as a chemical intermediate. The National Cancer Institute nominated diisopropylcarbodiimide for study as a representative chemical in the alkylcarbodiimide class because of its acute toxicity; its use in chemical, pharmaceutical, and recombinant DNA industries; and the absence of data on potential health effects. Male and female F344/N rats and B6C3F1 mice were administered diisopropylcarbodiimide (greater than 99% pure) dermally for 2 weeks, 3 months, or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium, rat and mouse bone marrow cells, and mouse peripheral blood erythrocytes. 2-WEEK STUDY IN RATS: Groups of five male and five female F344/N rats were dermally administered 0.3 mL ethanol containing 0, 3, 9, 27, or 81 mg diisopropylcarbodiimide or 0.3 mL of the neat chemical containing 242 mg per animal, 5 days a week for 2 weeks. All rats in the 27, 81, and 242 mg groups died before the end of the study. Of the surviving groups, final body weights were similar to those of the vehicle controls. Clinical findings included convulsions/seizures, nasal/eye discharge, tremors, and comatose conditions in 81 and 242 mg rats and lethargy, ataxia, and abnormal breathing in 27 mg rats. The incidences of epidermal hyperplasia at the site of application in 9 and 27 mg males and 27 mg females were significantly greater than those in the vehicle controls; the incidences of hyperkeratosis in 3 and 9 mg males and 9 mg females were also significantly increased. 2-WEEK STUDY IN MICE: Groups of five male and five female B6C3F1 mice were dermally administered 0.1 mL ethanol containing 0, 1, 3, 9, or 27 mg diisopropylcarbodiimide or 0.1 mL of the neat chemical containing 81 mg per animal, 5 days a week for 2 weeks. All 9, 27, and 81 mg mice died before the end of the study. Final body weights of the surviving groups were similar to those of the vehicle controls. Clinical findings in 9, 27, and 81 mg mice included comatose conditions, convulsions/seizures, tremors, abnormal breathing, nasal/eye discharge, lethargy, and irritation at the site of application. Incidences of chronic active inflammation at the site of application in 9 mg males and females were significantly greater than those in the vehicle control groups. 3-MONTH STUDY IN RATS: Groups of 10 male and 10 female core study F344/N rats were dermally administered 0, 10, 20, 40, 80, or 160 mg diisopropylcarbodiimide/kg body weight in ethanol, 5 days per week for 3 months. Groups of 10 male and 10 female clinical pathology rats were administered the same doses for 22 days. All 160 mg/kg core study rats were sacrificed moribund or died within the first week of the study. All 80 mg/kg rats died or were found moribund by day 59. Significant decreases in body weight gain occurred in 40 mg/kg males and females, and a significant decrease in final mean body weight occurred in 40 mg/kg females. Clinical findings in groups administered 40 mg/kg or more generally included irritation of the skin at the site of application, seizures, ataxia, abnormal breathing, ruffled fur, thinness, and lethargy. Significantly increased incidences of skin lesions at the site of application included epidermal hyperplasia in all dosed groups of males (except 160 mg/kg) and 40 mg/kg or greater females, epidermal necrosis in 160 mg/kg males and females, and chronic active inflammation in 80 and 160 mg/kg males and females. Significantly increased incidences of nonneoplastic lesions occurred in the brain, lung, and liver (males only) of rats administered 80 or 160 mg/kg. 3-MONTH STUDY IN MICE Groups of 10 male and 10 female B6C3F1 mice were dermally administered 0, 17.5, 35, 70, 140, or 280 mg/kg diisopropylcarbodiimide in ethanol, 5 days per week for 3 months. All mice in the 280 mg/kg group and nine males and nine females in the 140 mg/kg group died before the end of the study. The final mean body weight gain of 70 mg/kg males was significantly less than that of the vehicle control group. Clinical findings observed in 140 and 280 mg/kg mice included abnormal breathing, ataxia, comatose conditions, convulsions/seizures, irritation at the site of application, lethargy, ruffled fur, and thinness. Significant increases in kidney weights occurred in 17.5 and 35 mg/kg males. Significant decreases in total spermatid heads per testis and average spermatid count occurred in 17.5 mg/kg males. At the site of application, the incidences of epidermal hyperplasia in males and females administered 70 mg/kg or greater, chronic inflammation in 140 and 280 mg/kg males and 70 mg/kg or greater females, and sebaceous gland hyperplasia in 140 mg/kg males were significantly increased. Thymic atrophy was significantly increased in 140 and 280 mg/kg males and females. 2-YEAR STUDY IN RATS: Groups of 50 male and 50 female F344/N rats were dermally administered 0, 10, 20, or 40 mg/kg diisopropylcarbodiimide in anhydrous ethanol 5 days per week for 2 years. Survival of 20 mg/kg males was significantly greater than that of the vehicle controls; survival of all dosed groups of females was similar to that of the vehicle controls. Body weights of 40 mg/kg rats were generally less than those of the vehicle controls after week 13. Clinical findings frequently observed in 40 mg/kg males included ataxia, excitability, impaired gait, low muscle tone, abnormal breathing, lethargy, vocalization, and seizures. Because of severe neurological signs exhibited by the 40 mg/kg males, a neuropathological review of these animals was performed. The principal pathological findings of the brain included neuronal necrosis, hemorrhage, and/or fibrinoid arteriole necrosis. Incidences of hemorrhage in the lung of 40 mg/kg males, chronic lung inflammation in 10 and 20 mg/kg females, and alveolar epithelium hyperplasia in 20 mg/kg females were significantly greater than those of the vehicle controls. At the site of application, the incidences of epidermal hyperplasia in all dosed groups of males and 20 and 40 mg/kg females and chronic inflammation in all dosed groups of males and 40 mg/kg females were significantly increased. There was no increased incidences of neoplasms related to diisopropylcarbodiimide administration. 2-YEAR STUDY IN MICE: Groups of 50 male and 50 female B6C3F1 mice were dermally administered 0, 10, 20, or 40 mg/kg diisopropylcarbodiimide in anhydrous ethanol, 5 days per week for 2 years. Survival of all dosed groups was similar to that of the vehicle control groups. Mean body weights of dosed groups of mice were generally similar to those of the vehicle control groups throughout the study. There were no increased incidences of neoplasms that were attributed to the administration of diisopropylcarbodiimide. Significantly increased incidences of epidermal hyperplasia and focal dermal inflammation of the skin at the site of application occurred in 20 mg/kg male mice. GENETIC TOXICOLOGY: Diisopropylcarbodiimide was not mutagenic in Salmonella typhimurium strains TA97, TA98, TA100, or TA1535 with or without liver S9 activation enzymes. In vivo, the frequency of micronucleated normochromatic erythrocytes was significantly increased in male and female mice after 3 months of dermal exposure to diisopropylcarbodiimide. In addition, significantly elevated frequencies of micronucleated polychromatic erythrocytes (reticulocytes) and micronucleated normochromatic erythrocytes were seen in male mice during a 4-month dermal exposure to diisopropylcarbodiimide. Negative results were obtained, however, in an acute three-injection rat bone marrow micronucleus study. A three-treatment acute micronucleus test in male mice also showed no increase in micronucleated erythrocytes, but results of a single injection micronucleus test in male mice were concluded to be equivocal, due to an increase in micronucleated erythrocytes seen in peripheral blood but not in bone marrow preparations. CONCLUSIONS: Under the conditions of these 2-year dermal studies, there was no evidence of carcinogenic activity of diisopropylcarbodiimide in male or female F344/N rats or B6C3F1 mice administered 10, 20, or 40 mg/kg. Clinical and histological signs of neurotoxicity in male rats were associated with diisopropylcarbodiimide administration.     

1,2,3-Trichloropropane: A Multisite Carcinogen in Rats and Mice

1,2,3-Trichloropropane was evaluated in 2-year toxicology andcarcinogenesis studies by the National Toxicology Program. Theselection of this chemical for study was based on the potentialfor human exposure, its positive in vitro genotoxicity, andthe carcinogenicity of structurally related chemicals. Duringthe 2-year study 1,2,3-trichloropropane was administered incorn oil by gavage 5 days per week; groups of 60 F344/N ratsreceived 0, 3, 10, or 30 mg/kg, while groups of 60 B6C3F1 micereceived 0, 6, 20, or 60 mg/kg. Because of reduced survivalassociated with the development of chemical-related neoplasms,rats that received 30 mg/kg were terminated at 65 weeks (females)or 76 weeks (males). Similarly, mice that received 60 mg/kgwere terminated at 73 weeks (females) or 79 weeks (males), whilegroups of mice that received 20 mg/kg were terminated at 88weeks. 1,2,3-Trichloropropane induced benign and/or malignantneoplasms at multiple sites in both rats and mice; this includedincreased incidences of benign and malignant neoplasms of thesquamous epithelium of the oral mucosa and forestomach of maleand female rats, benign neoplasms of the kidney and pancreasand benign or malignant neoplasms of the preputial gland inmale rats, malignant neoplasms of the mammary gland, and benignor malignant neoplasms of the clitoral gland in female rats.In mice, 1,2,3-trichloropropane induced a low incidence of malignantneoplasms of the oral mucosa in females, high incidences ofbenign and malignant neoplasms of the forestomach in males andfemales, benign neoplasms of the liver and harderian gland ofmales and females, and uterine neoplasms in females.