National Toxicology Program technical report series最新文献

Unlabelled: 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

Unlabelled: Sodium dichromate dihydrate is one of a number of inorganic compounds containing hexavalent chromium (Cr VI) found in drinking water source supplies as a contaminant resulting from various industrial processes including electroplating operations, leather tanning, and textile manufacturing. Because of the lack of adequate experimental data on the toxicity and carcinogenicity of hexavalent chromium ingested orally and because hexavalent chromium has been found in drinking water source supplies, the California Congressional Delegation, the California Environmental Protection Agency, and the California Department of Health Services nominated hexavalent chromium to the National Toxicology Program for study. Results of 3 month toxicity studies in F344/N rats and B6C3F1, BALB/c, and am3-C57BL/6 mice were reported earlier in NTP Toxicity Report 72. In the current study, male and female F344/N rats and B6C3F1 mice were exposed to sodium dichromate dihydrate (greater than 99.7% pure) in drinking water for 2 years. 2-YEAR STUDY IN RATS: Groups of 50 male and 50 female rats were exposed to drinking water containing 0, 14.3, 57.3, 172, or 516 mg/L sodium dichromate dihydrate (equivalent to 0, 5, 20, 60, or 180 mg/L chromium) for 2 years (equivalent to average daily doses of approximately 0.6, 2.2, 6, or 17 mg sodium dichromate dihydrate/kg body weight for males and 0.7, 2.7, 7, or 20 mg/kg for females). Survival of exposed groups was similar to that of the control groups. Mean body weights of 516 mg/L males and females were less than those of the controls throughout the study. The lower body weights were partly attributed to poor palatability of the dosed water and consequent reductions in water consumption. Water consumption by 172 and 516 mg/L rats was less than that by the controls throughout the study. Exposure to sodium dichromate dihydrate caused a microcytic hypochromic anemia in rats that ameliorated with time. Exposure to sodium dichromate dihydrate resulted in the development of neoplasms of the squamous epithelium that lines the oral mucosa and tongue. The incidences of squamous cell carcinoma in the oral mucosa of 516 mg/L male and female rats were significantly greater than those in the controls. The incidence in 172 mg/L females exceeded the historical control ranges for drinking water studies and for all routes of administration. The incidences of squamous cell papilloma or squamous cell carcinoma (combined) of the oral mucosa or tongue of 516 mg/L male and female rats were significantly greater than those in the controls. Exposure concentration-related nonneoplastic liver lesions were observed in males and females exposed to 57.3 mg/L or greater. These included histiocytic cellular infiltration, chronic inflammation, fatty change (females), basophilic focus (males), and clear cell focus (females). Increased incidences of histiocytic cellular infiltration also occurred in the small intestine (duodenum), mesenteri

Unlabelled: Methylene blue trihydrate has a variety of biomedical and biologically therapeutic applications. Methylene blue trihydrate was nominated by the National Cancer Institute (NCI) for carcinogenicity testing based on the numerous uses of this compound and the lack of long-term toxicity data, including epidemiological studies of methylene blue trihydrate, as well as the inadequate animal data on this compound. Male and female F344/N rats and B6C3F1 mice were administered methylene blue trihydrate in 0.5% aqueous methylcellulose by gavage for 1 month, 3 months, or 2 years. Genetic toxicology studies were conducted using Salmonella typhimurium, Escherichia coli, cultured Chinese hamster ovary cells, mouse bone marrow cells, and mouse peripheral blood erythrocytes. 1-MONTH STUDY IN RATS: Groups of 10 male and 10 female core study rats and groups of 10 male and 10 female clinical pathology study rats were administered methylene blue trihydrate in 0.5% aqueous methylcellulose solution by gavage at doses of 0, 125, 250, 500, 1,000, or 2,000 mg/kg, 5 days per week for 5 weeks. In the 500 mg/kg groups, one male died the first week of the study and one male and four females died the second week of the study. All rats in the 1,000 mg/kg group died by study day 10, and all rats in the 2,000 mg/kg group died by study day 6. Final mean body weights of male and female rats in the 250 and 500 mg/kg groups were significantly less than those of the vehicle controls. Dosed rats developed methemoglobinemia and a regenerative Heinz body anemia. Significant increases in spleen weights occurred in all surviving dosed groups. There were also significant decreases in the thymus weights of 250 and 500 mg/kg males and 125 and 250 mg/kg females. Spleen lesions associated with methylene blue trihydrate administration included hematopoietic cell proliferation, pigmentation, lymphoid depletion of the lymphoid follicles, and capsular fibrosis. Hyperplasia of the bone marrow occurred in all dosed groups of rats. Liver lesions associated with methylene blue exposure included centrilobular necrosis in rats dying early, hematopoietic cell proliferation, and Kupffer cell pigmentation with erythrophagocytosis. 1-MONTH STUDY IN MICE: Groups of 10 male and 10 female core study mice were administered methylene blue trihydrate in 0.5% aqueous methylcellulose solution by gavage at doses of 0, 125, 250, 500, 1,000, or 2,000 mg/kg, 5 days per week for 5 weeks. None of the mice in the 500, 1,000, and 2,000 mg/kg groups survived to the end of the study. In the 250 mg/kg groups, two females died on days 16 and 18 and two males died on days 6 and 13. Mean body weights of surviving dosed mice were similar to those of the vehicle controls. Thinness, abnormal respiration, hypothermia, lethargy, ataxia, and ruffled fur were observed in a few surviving animals in the 250 mg/kg groups. Hypothermia and abnormal posture were observed in mice in the 500, 1,000, and 2,000 mg/k

Genistein is a naturally occurring isoflavone that interacts with estrogen receptors and multiple other molecular targets. Human exposure to genistein is predominantly through consumption of soy products, including soy-based infant formula and dietary supplements. Consumption of soy and genistein has been associated with a variety of beneficial effects in animals and humans, but concerns have also been raised concerning potential adverse effects of genistein, particularly with regard to reproductive toxicity and the induction or potentiation of carcinogenesis, due primarily to its weak estrogenic activity. Because of these concerns, genistein was selected as one of the compounds to be examined in a protocol utilizing Sprague-Dawley rats to evaluate the effects of multigenerational and long-term exposures to doses of estrogenic agents that produce subtle reproductive tract lesions in developmentally exposed Sprague-Dawley rat pups. Results from the multigenerational reproductive toxicology feed study are reported in this report, and results of the 2-year feed study are reported separately (NTP, 2008a). Data from a preliminary reproductive dose range-finding feed study (NTP, 2007) that utilized exposure concentrations of up to 1,250 ppm genistein were used to select dietary exposure concentrations of 0, 5, 100, and 500 ppm for the current study. These dietary doses resulted in ingested genistein doses of approximately 0, 0.3, 7, or 35 mg genistein/kg body weight per day for males and 0, 0.5, 10, or 51 mg/kg per day for females during the time that the rats were directly consuming dosed feed. The current study was a multigenerational study (F(0) through F(4), with F(5) litters terminated at weaning) focused on reproductive endpoints. Animals were continuously exposed to genistein from the time that the F(0) generation was 6 weeks old through weaning of the F(3) generation, and animals of the F(0) through F(4) generations were sacrificed and necropsied on postnatal day 140 (PND 140). Dosed feed was removed from the F(3) pups at the time of weaning, and this generation and subsequent generations were maintained on control feed for the remainder of the study. For this study, 140 animals of each sex were obtained from the NCTR CD (Sprague-Dawley) rat colony at weaning and placed on a soy- and alfalfa-free diet that was used throughout the study in an attempt to maintain consistently low background exposure to phytoestrogens. Thirty-five animals per sex were assigned to exposure groups by a weight-ranked randomization procedure prior to the start of dietary exposure of the parental (F(0)) generation at 6 weeks of age. At the time of mating, males were paired with females from the same exposure group, and they were housed together until evidence of successful mating was detected or for a maximum of 14 days. Litters were randomly standardized to four males and four females on PND 2, and 25 litters per exposure group and their associated sires and dam

Unlabelled: Genistein is a naturally occurring isoflavone that interacts with estrogen receptors and multiple other molecular targets. Human exposure to genistein is predominantly through consumption of soy products, including soy-based infant formula and dietary supplements. Consumption of soy and genistein has been associated with a variety of beneficial effects in animals and humans, but concerns have also been raised regarding potential adverse effects of genistein, particularly with regard to reproductive toxicity and the induction or potentiation of carcinogenesis, due primarily to its weak estrogenic activity. Because of these concerns, genistein was selected as one of the compounds to be examined using a protocol designed to evaluate the effects of multigenerational and long-term exposures to doses of estrogenic agents that produce subtle reproductive tract lesions in developmentally exposed Sprague-Dawley rat pups. Results from the 2-year study are reported here, and results from the multigenerational reproductive toxicology feed study are reported separately (NTP, 2008a). Data from a preliminary dose range-finding feed study (NTP, 2007) that utilized exposure concentrations up to 1,250 ppm genistein were used to select dietary exposure concentrations of 0, 5, 100, and 500 ppm for the current study. The multigenerational reproductive toxicology study examined F(0) through F(4) generations with F(5) litters terminated at weaning and focused on reproductive endpoints (NTP, 2008a). Animals were exposed from the time that the F(0) generation was 6 weeks old through weaning of the F(3) generation, and animals of the F(0) through F(4) generations were necropsied at 20 weeks of age. The current study was a 2-year dietary study utilizing three exposure arms: continuous exposure from conception through 2 years (designated F(1) continuous, or F(1)C), exposure from conception through 20 weeks followed by control diet to 2 years [designated F(1) truncated at postnatal day (PND) 140, or F(1)T140], and exposure from conception through weaning followed by control diet to 2 years (designated F(3) truncated at PND 21, or F(3)T21). The "F(3)" designation for the F(3)T21 arm indicates that these animals were siblings of the F(3) animals from the multigenerational reproductive toxicology study (NTP, 2008a). The F(1)C and F(1)T140 animals were also siblings but were derived from a separate breeding that was identical to the procedure used to produce the F(1) generation of the multigenerational reproductive toxicology study. The animals in this study were exposed to genistein during various phases of their lives from conception until termination at 2 years, and the ingested doses varied over the course of the study. During pregnancy, the ingested doses of the dams were approximately 0, 0.5, 9, or 45 mg/kg body weight per day. During lactation, the dams' ingested doses were 0, 0.7, 15, or 75 mg/kg per day. Supplementary studies, which are d

Unlabelled: alpha-Methylstyrene is used in the production of acrylonitrile-butadiene-styrene resins and copolymers, which improve the impact and heat-resistant properties of polymers, specialty grades of plastics, rubber, and protective coatings. alpha-Methylstyrene also moderates polymerization rates and improves product clarity in coatings and resins. Low molecular weight liquid polymers are used as plasticizers in paints, waxes, adhesives, and plastics. alpha-Methylstyrene was nominated by the U.S. Environmental Protection Agency for toxicologic evaluation and genotoxicity studies based on its high production volume and limited information available on its toxicity. Male and female F344/N rats and B6C3F1 mice were exposed to alpha-methylstyrene (99.5% pure) by inhalation for 3 months or 2 years. Inhalation studies were conducted because the primary route of human exposure is via inhalation. Genetic toxicology studies were conducted in Salmonella typhimurium, cultured Chinese hamster ovary cells, and mouse peripheral blood erythrocytes. 3-MONTH STUDY IN RATS: Groups of 10 male and 10 female rats were exposed by whole-body inhalation to alpha-methylstyrene at concentrations of 0, 75, 150, 300, 600, or 1,000 ppm for 6 hours per day, 5 days per week for 14 weeks. Additional clinical pathology groups of 10 male and 10 female rats were exposed to the same concentrations for 23 days. All rats survived to the end of the study, and mean body weights of all exposed groups were similar to those of the chamber controls. Kidney weights were significantly increased in 1,000 ppm males and 600 and 1,000 ppm females. Statistically significant increases in liver weights occurred in 150 ppm or greater males and 600 and 1,000 ppm females. The incidences of renal hyaline droplet accumulation were similar between exposed groups and chamber control groups, but the severity of hyaline droplet accumulation in 600 and 1,000 ppm males was greater than in chamber controls. Consistent with the hyaline droplet accumulation, an exposure-related increase in alpha2μ-globulin was detected in the kidneys of males exposed to alpha-methylstyrene. Morphologic changes were not detected in the liver. 3-MONTH STUDY IN MICE: Groups of 10 male and 10 female mice were exposed by whole-body inhalation to alpha-methylstyrene at concentrations of 0, 75, 150, 300, 600, or 1,000 ppm for 6 hours per day, 5 days per week for 14 weeks. Two female mice in the 1,000 ppm group died before exposure on day 3. Final mean body weights of 600 and 1,000 ppm males and 75, 300, and 1,000 ppm females were significantly less than those of the chamber controls; final mean body weight gains of mice exposed to 300 ppm or greater were also significantly less. Moderate to severe sedation (males only) and ataxia were observed in 1,000 ppm mice. The absolute liver weights of 600 and 1,000 ppm females and the relative liver weights of 300, 600, and 1,000 ppm males and females were significantly

Unlabelled: Acidic solutions have been used for decades to treat a variety of skin conditions. Many of these solutions consist of organic acids with a hydroxy group on a carbon adjacent to the carbonyl carbon and are referred to as alpha-hydroxy acids (AHA). Organic acids with hydroxy groups on the second carbon from the carbonyl carbon are referred to as beta-hydroxy acids (BHA). Both AHA and BHA are used to treat various skin conditions. One of the most widely used AHA is glycolic acid, while salicylic acid is a commonly used BHA. Chemical peels containing 20% to 70% glycolic acid have been used by dermatologists to treat ichthyosis, acne, xerosis, actinic keratosis, seborrheic keratoses, warts, and psoriasis. AHA have recently been used to treat photoaged skin and are now included in many commercially available cosmetic skin treatments. When used in a formulation for a chemical peel, topical treatment of skin with AHA and BHA can result in removal of the stratum corneum, alteration of the skin's histology, and increased cell proliferation in the basal layer of the epidermis. Since AHA and BHA are used to correct photoaged skin, and since exposure to sunlight of skin treated with AHA or BHA is likely, studies were designed to determine the effects of topical application of creams containing AHA (0%, 4%, or 10% glycolic acid, pH 3.5) or BHA (0%, 2%, or 4% salicylic acid, pH 4.0) on the photocarcinogenesis of simulated solar radiation using a filtered 6.5 kW xenon arc light source [simulated solar light (SSL)]. Male and female Crl:SKH-1 (hr-/hr-) hairless mice were exposed to glycolic acid or salicylic acid alone or in combination with SSL for 40 weeks, and the mice were followed for an additional 12 weeks. 1-YEAR STUDY IN MICE: Groups of 36 male and 36 female mice were exposed to 0.0, 0.3, 0.6, or 0.9 minimal erythema dose (MED) of SSL during the afternoon (1200 to 1600 hours) 5 days per week for 40 weeks. Groups of 18 male and 18 female mice were treated in the morning (0800 to 1100 hours) with 2 mg/cm2 control cream, 4% glycolic acid cream, 10% glycolic acid cream, 2% salicylic acid cream, or 4% salicylic acid cream on the dorsal skin, and in the afternoon (1200 to 1600 hours) with 0.3 MED of SSL 5 days per week for 40 weeks. Additional groups of 18 male and 18 female mice were treated in the morning (0800 to 1100 hours) with 2 mg/cm2 control cream, 4% glycolic acid cream, 10% glycolic acid cream, 2% salicylic acid cream, or 4% salicylic acid cream on the dorsal skin, and in the afternoon (1200 to 1600 hours) with 0.6 MED of SSL 5 days per week for 40 weeks. All mice were held an additional 12 weeks following the end of treatment. There were no effects of SSL exposure or topical treatment on the body weights of the mice. Increasing doses of SSL resulted in an SSL-dose trend in survival, with the greatest dose of SSL causing the earliest removal. This effect was present in both the untreated and control cream treated mice. T

Unlabelled: Dibromoacetic acid is a water disinfection by-product. Dibromoacetic acid was nominated to the National Toxicology Program by the United States Environmental Protection Agency for toxicity and carcinogenicity studies in rats and mice because of widespread human exposure and because a related dihaloacetate, dichloroacetate, was found to be carcinogenic to the liver of rats and mice. Drinking water was selected as the route of exposure to mimic human exposure to this chemical. Male and female F344/N rats and B6C3F1 mice were exposed to dibromoacetic acid (greater than 99% pure) in drinking water for 2 weeks, 3 months, or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium and peripheral blood erythrocytes of exposed mice. 2-WEEK STUDY IN RATS: Groups of five male and five female rats were exposed to 0, 125, 250, 500, 1,000, or 2,000 mg/L dibromoacetic acid in drinking water for 2 weeks, equivalent to average daily doses of approximately 17, 32, 67, 134, 270 (males), or 257 (females) mg dibromoacetic acid/kg body weight. All rats survived to the end of the study. Mean body weight gains of 1,000 mg/L males and of 500 mg/L females were significantly greater than those of the controls. Water consumption by exposed and control groups was similar. Liver weights of exposed males and females were significantly increased. Right testis weights of males exposed to 500 mg/L or greater were significantly decreased. The incidences of hepatocytic cytoplasmic alteration were significantly increased in males exposed to 500 mg/L or greater and in 2,000 mg/L females. Testicular lesions, characterized by a delay in spermiation and retained spermatids, were noted in males exposed to 500 mg/L or higher concentrations. 2-WEEK STUDY IN MICE: Groups of five male and five female mice were exposed to 0, 125, 250, 500, 1,000, or 2,000 mg/L dibromoacetic acid (equivalent to average daily doses of approximately 24, 47, 95, 178, or 370 mg/kg to males and 22, 53, 88, 166, or 309 mg/kg to females) in drinking water for 2 weeks. All mice survived to the end of the study. Mean body weight gains of 250 and 500 mg/L males were significantly greater than those of the controls. Water consumption by exposed and control groups was similar. Liver weights of males and females in the 1,000 and 2,000 mg/L groups were significantly increased. Thymus weights of males and females in the 1,000 and 2,000 mg/L groups were significantly less than those of controls. The incidences of thymus atrophy were significantly increased in 1,000 and 2,000 mg/L males and 2,000 mg/L females. The incidences of morphological changes to the germinal epithelium of the testes were increased in males exposed to 1,000 or 2,000 mg/L. 3-MONTH STUDY IN RATS: Groups of 10 male and 10 female rats were exposed to 0, 125, 250, 500, 1,000, or 2,000 mg/L dibromoacetic acid (equivalent to average daily doses of approximately 10, 20, 40, 90, and 166 mg/kg to males and 12, 2

Unlabelled: Methyl isobutyl ketone is used as a denaturant for rubbing alcohol; as a solvent for paints, varnishes, nitrocellulose, lacquers, and protective coatings; in industrial extraction processes; in dry-cleaning preparations; and in the synthesis of methyl isobutyl carbinol. Methyl isobutyl ketone was nominated for study by the National Cancer Institute and the United States Environmental Protection Agency because of its widespread use, the high potential for worker exposure due to its many industrial applications, and its high production volume. Male and female F344/N rats and B6C3F1 mice were exposed to methyl isobutyl ketone (greater than 99% pure) by inhalation for 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium. 2-YEAR STUDY IN RATS: Groups of 50 males and 50 females were exposed to methyl isobutyl ketone at concentrations of 0, 450, 900, or 1,800 ppm by inhalation, 6 hours plus T(90) (12 minutes) per day, 5 days per week for 104 weeks. Survival of males exposed to 1,800 ppm was significantly less than that of the chamber controls. The mean body weights of the 900 and 1,800 ppm males were less than those of the chamber controls after weeks 97 and 89, respectively. In the standard evaluation of the kidney, there were slightly increased incidences of renal tubule adenoma and renal tubule adenoma or carcinoma (combined) in males exposed to 900 or 1,800 ppm, and renal tubule carcinoma in males exposed to 1,800 ppm. The incidences of renal tubule hyperplasia were also significantly increased in the 450 and 1,800 ppm males, and the severities were greater than in the chamber controls. Chronic nephropathy occurred in all males exposed to 1,800 ppm and in 70% to 88% of exposed females, and the severity was increased in 1,800 ppm males. The incidences of transitional epithelial hyperplasia of the renal pelvis in males exposed to 900 or 1,800 ppm and mineralization of the renal papilla in all groups of exposed males were significantly increased. In addition, two female rats exposed to 1,800 ppm had renal mesenchymal tumors. In the extended evaluation of the kidney, renal tubule adenomas and renal tubule hyperplasia occurred in all groups of exposed male rats. In the combined single and step section analysis, the incidences of renal tubule adenoma and renal tubule adenoma or carcinoma (combined) were significantly increased in males exposed to 1,800 ppm. The incidences of renal tubule hyperplasia were also significantly increased in all exposed groups of males. There was a positive trend in the incidences of mononuclear cell leukemia in males, and the incidence in the 1,800 ppm group was significantly increased. The incidence of adrenal medulla hyperplasia in the 1,800 ppm males was significantly increased. 2-YEAR STUDY IN MICE: Groups of 50 males and 50 females were exposed to methyl isobutyl ketone at concentrations of 0, 450, 900, or 1,800 ppm by inhalation, 6 hours plus T(90) (12 minutes) per

Unlabelled: 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 female