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NTP Comparative Initiation/Promotion Skin Paint Studies of B6C3F1 Mice, Swiss (CD-1(R)) Mice, and SENCAR Mice.

In 1983, an ad hoc panel on chemical carcinogenesis testing and evaluation recommended additional methods that should be used by the National Toxicology Program (NTP) for the detection and evaluation of chemical carcinogens. One recommendation was that there should be an increased emphasis on short-term tests to detect agents that do not exert genetic effects such as some promoting agents. Initiation/promotion models have been used routinely to identify chemicals with promoting potential and to study tumorigenesis. In one model, a topical subcarcinogenic dose of a chemical is first applied to the back of the skin (initiation) followed by repeated topical applications of one or more chemicals (promotion) and the skin is monitored for tumor development. Mouse skin has been shown to be more responsive (i.e., develops tumors using this protocol) than other commonly used laboratory rodent models. However, not all mouse strains are equally sensitive. The skin tumor response of the B6C3F1 mouse using the initiation/promotion protocol was not known. Since the B6C3F1 mouse is commonly used in NTP carcinogenesis studies and much is known of its biology and response to chemical carcinogens, known initiators and promoters were used to compare the tumor response sensitivity of B6C3F1 mouse skin to that of two often-used responsive strains, Swiss (CD-1(R)) and SENCAR mice. The combination of 7,12- dimethylbenz(a)anthracene (DMBA) initiation and 12-O-tetradecanoylphorbol-13- acetate (TPA) promotion was selected because this pair is routinely used to study tumorigenesis. However, DMBA requires metabolic activation to achieve initiation and it was possible that the B6C3F1 mouse metabolism might not make this conversion (DiGiovanni and Juchau, 1980). Therefore, a second study was conducted using N-methyl-N'-nitro-N-nitrosoguanidine (MNNG), a direct acting carcinogen, as the initiator. MNNG is not used as frequently for mouse skin studies as is DMBA. In addition to the promoter TPA, benzoyl peroxide (BPO), a non-phorbol ester and known promoter after DMBA initiation, was also used (Slaga et al., 1981). Each initiating chemical was used in combination with each promoting chemical as described on the study design table below. Additional groups of male and female mice of each strain were treated with repeated applications of acetone (vehicle control), repeated applications of promoter (TPA or BPO) without prior initiation treatment (promoter reference controls), or a single application of the initiator (DMBA or MNNG) followed by repeated applications of acetone (initiator controls). All three strains of mice demonstrated sensitivity by developing skin tumors after topical application of the chemicals under study (DMBA, MNNG, TPA, and BPO). The most sensitive of the three strains appeared to be SENCAR mice, in the sense that lower doses of the test chemical were generally required to produce effects equivalent to those in the other two strains. Skin tumors also tended to develop earlier and with greater multiplicity in SENCAR mice than in the other two strains. By these criteria, the overall sensitivity of Swiss (CD-1(R)) mice was intermediate, and B6C3F1 mice showed the least overall sensitivity to dermal carcinogenicity. In response to recommendations regarding specific short-term tests and also on the skin tumor response sensitivity of various initiators and promoters, SENCAR mice would be the most acceptable strain to use for such studies. Though the B6C3F1 mice were less responsive in the skin initiation/promotion protocol, promotion data from this strain may, at times, be of more use in explaining mechanisms of tumor development (e.g. when there is a strain specific response observed in 2-year carcinogenicity studies or effects on melanocytes are suspected). See the full report or study abstract for table of Study Design for the 1-Year Comparative Initiation/Promotion Skin Paint Studies. The 1-year complete carcinogen studies used repeated applications of low concentrations of the carcinogens DMBA and MNNG. The skin tumor response in aln all three strains under these conditions was more similar than in the initiation and promotion studies. There was a high incidence of skin tumors in all three strains with both carcinogens. More B6C3F1, and SENCAR mice developed skin tumors and averaged more tumors per mouse than did Swiss (CD-1®) mice. Skin tumors developed earlier in SENCAR mice than in B6C3F1 and Swiss (CD-1®) mice. Although B6C3F1 mice exhibited the lowest overall sensitivity to the initiation/promotion protocol when compared to Swiss (CD-1®) and SENCAR mice, the response of B6C3F1 mice was similar to Swiss (CD-1®) and SENCAR mice for complete carcinogen studies.

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of 1-Amino-2,4-Dibromoanthraquinone (CAS No. 81-49-2) in F344/N Rats and B6C3F1 Mice (Feed Studies).

1-Amino-2,4-dibromoanthraquinone is an anthraquinone-derived vat dye, a member of a class of insoluble dyes that are impregnated into textile fibers. Five anthraquinone-derived dyes with representative and diverse structures, as well as the parent chemical, anthraquinone, were selected for NTP Toxicology and Carcinogenesis evaluation. Similar to the benzidine dye initiative, the rationale for selecting these vat dyes was to generate sufficient toxicologic data to permit more reliable predictions of carcinogenicity to be made on other chemicals in this class, thereby eliminating or reducing the need to study every anthraquinone dye. 1-Amino-2,4-dibromoanthraquinone is the last anthraquinone-derived dye in this group to be studied. Groups of male and female F344/N rats and B6C3F1 mice were exposed to 1-amino-2,4-dibromoanthraquinone (87% to 97% pure) for 13 weeks or for 9, 15, or 24 months. Because 1-amino-2,4-dibromoanthraquinone was predicted to be carcinogenic, these studies were designed to evaluate the potential for tumor progression and regression. Absorption and excretion studies were carried out in male F344/N rats. Genetic toxicity was determined in vitro using Salmonella typhimurium and cultured Chinese hamster ovary cells. Extensive chemical analyses were performed to identify and characterize impurities of the 1-amino-2,4-dibromoanthraquinone used in these studies. 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female rats were given 0, 2,500, 5,000, 10,000, 25,000, or 50,000 ppm 1-amino-2,4-dibromoanthraquinone in feed for 13 weeks. These levels correspond to approximately 150 to 3,200 mg 1-amino-2,4-dibromoanthraquinone/kg body weight per day for males and to approximately 170 to 3,200 mg/kg for females. Chemical-related mortality was limited to one male and one female in the 50,000 ppm groups. Final mean body weights and body weight gains of all exposed groups of rats were significantly lower than those of the controls. Feed consumption by all exposed groups was less than that by the controls throughout the study and generally decreased with increasing exposure concentration. Pink-red staining of the fur and tail was observed in all exposed groups. Absolute and relative liver weights of all exposed groups were generally significantly greater than those of the controls. Chemical-related lesions were present in the liver, kidney, and spleen of male and female rats. Nonneoplastic lesions in the liver included foci of hepatocellular alteration, diffuse hepatocellular hypertrophy (cytomegaly), hepatocellular cytoplasmic vacuolation, bile duct hyperplasia, inflammation, and pigmentation. These differences were observed primarily in the 25,000 and 50,000 ppm groups of males and females; the spectrum of proliferative lesions of the bile ducts (hyperplasia, fibrosis, and necrotizing cholangitis) in the 25,000 and 50,000 ppm groups was morphologically consistent with the lesion described as cholangiofibrosis. Pigmentation was present in the renal tubule epithelium of all groups of exposed rats; nuclear enlargement (karyomegaly) was also present in the renal tubule epithelium in some of the exposed rats. Accumulation of hyaline droplets in the cytoplasm of the renal tubule epithelium and tubule lumina was present in 2,500, 5,000, 10,000, and 25,000 ppm males. Incidences of hematopoiesis of the spleen in exposed groups of males and females were increased compared to those in the controls. 13-WEEK STUDY IN MICE: Groups of 10 male and 10 female mice were given 0, 2,500, 5,000, 10,000, 25,000, or 50,000 ppm 1-amino-2,4-dibromoanthraquinone in feed for 13 weeks. These levels correspond to approximately 500 to 10,600 mg 1-amino-2,4-dibromoanthraquinone/kg body weight per day for males and approximately 660 to 11,700 mg/kg per day for females. There was no chemical-related mortality. Feed consumption and final mean body weights of exposed groups were similar to those of the controls. Red staining of the fur was observed in all exposed groups. Absolute and relative liver weights of the exposed groups were greater than those er than those of the controls except for the absolute liver weight of 2,500 ppm males. Absolute and relative kidney weights of 25,000 and 50,000 ppm males were lower than those of the controls. Chemical-related lesions were limited to the livers of males and consisted of pigmentation of hepatocytes at all exposure concentrations and centrilobular hepatocellular hypertrophy at 10,000, 25,000, and 50,000 ppm. Minimal pigment was present in the liver of one female in the 25,000 ppm group and in one female in the 50,000 ppm group. 2-YEAR STUDY IN RATS: Groups of 70 male and 70 female rats were given 0, 5,000, or 10,000 ppm 1-amino-2,4-dibromoanthraquinone in feed for 103 weeks. In addition, groups of 50 male and 50 female rats were given 2,000 ppm 1-amino-2,4-dibromoanthraquinone in feed for 104 weeks. These exposure concentrations were approximately equal to 90, 240, or 490 mg 1-amino-2,4-dibromoanthraquinone/kg body weight for males and 110, 285, or 600 mg/kg for females. Ten animals from each group were evaluated for histopathology at 9 months. Additional groups of 10 animals from the 0 and 10,000 ppm groups were evaluated for histopathology at 15 months. Survival, Body Weights, Feed Consumption, and Clinical Findings In the 2-year study, survival of the 10,000 ppm males and females was significantly lower than that of the controls. Survival of the 2,000 and 5,000 ppm groups was similar to that of the controls. During the last year of the study, the mean body weights of exposed males were 80% to 91% those of controls, and the mean body weights of exposed females were 67% to 84% those of controls. Feed consumption among exposed groups was generally similar, but was less than that by controls. The fur and urine of all exposed male and female groups were discolored. Pathology Findings In the 2-year study, 1-amino-2,4-dibromoanthraquinone was associated with significant chemical-related increases in the incidences of benign and malignant neoplasms in the liver, large intestine, kidney, and urinary bladder of males and females. Chemical-related nonneoplastic proliferative and degenerative lesions occurred in the liver, kidney, urinary bladder, and forestomach of males and females. The incidences of foci of hepatocellular alteration and pigmentation in the liver of males and females were increased at the 9-month interim evaluation, and a hepatocellular adenoma was present in one 5,000 ppm male. At the 15-month interim evaluation, hepatocellular adenoma or carcinoma (combined) occurred in all males and nine females in the 10,000 ppm groups. By the end of the 2-year study, hepatocellular adenoma, carcinoma, cholangioma, or cholangiocarcinoma were observed in males and females in the 5,000 and 10,000 ppm groups. In the 2,000 ppm groups, similar liver neoplasms were present in 63% of the males and in 83% of the females. Of the hepatocellular carcinomas in the 5,000 and 10,000 ppm groups of males and females, 31% to 49% were metastatic to the lungs or other sites. Increases in the incidences of foci of hepatocellular alteration (basophilic, eosinophilic, and clear cell) and pigmentation of the liver were also observed in exposed groups of males and females. Adenomatous polyps (adenoma) of the large intestine were present in six 10,000 ppm males at the 15-month interim evaluation. Incidences of adenomatous polyp (adenoma) and carcinoma of the large intestine were significantly increased in exposed groups of males and females after 2 years; multiple benign and malignant intestinal neoplasms were observed in many of these rats. In the kidney, incidences of renal tubule adenoma and carcinoma were significantly increased in exposed groups of males and females after 2 years. Renal tubule adenomas were present in two 10,000 ppm males at 15 months. There were also chemical-related increases in the incidences and severities of renal tubule epithelial hyperplasia, pigmentation, and transitional cell hyperplasia in the kidney of males and females. Hyaline droplet accumulation was present in all exposed male rats at 9 months. Incidences of transitional cell papilloma and carcinoma of the urinary bladder were increased at 2 years in males and females in the 10,000 ppm groups. Transitional cell hyperplasia was observed in exposed males and females at the 15-month interim evaluation. Other nonneoplastic lesions observed in the urinary bladder at 2 years included metaplasia of the transitional epithelium and submucosal stromal tissue. In the forestomach, the incidences and severities of inflammation, ulceration, hyperkeratosis, and hyperplasia of the squamous mucosa were increased in all exposed groups of males and females at 2 years, but not at the 9- or 15-month interim evaluations. In exposed males and females, the incidences of mononuclear cell leukemia were significantly decreased. The incidences of atrophy of the seminal vesicle were increased in exposed male rats in the 2-year study. Stop-Exposure Evaluation in Rats Groups of 40 male and 40 female rats were given 20,000 ppm 1-amino-2,4-dibromoanthraquinone in feed for 9 or 15 months. At 9 months, 10 males and 10 females were evaluated for histopathology (9-month interim evaluation groups). After 9 months of exposure, an additional 10 males and 10 females were fed control diet until the end of the 15-month evaluation (9-month stop-exposure groups), and 20 males and 20 females continued to receive 20,000 ppm 1-amino-2,4-dibromoanthraquinone until the end of the evaluation (15-month exposure groups). The approximate daily consumption of 1-amino-2,4-dibromoanthraquinone was 1,335 mg/kg for males and 1,790 mg/kg for females in the 9-month stop-exposure groups and 1,115 mg/kg for males and 1,435 mg/kg for females in the 15-month exposure groups. Survival was similar among groups except for the females in the 15-month exposure group; the survival of this group was lower than that of the controls. Lower mean body weights were related to increased exposure duration. The mean body weights of exposed males were 76% to 82% that of controls, and the mean body weights of exposed females were 73% to 84% that of controls. For the stop-exposure evaluation, similar chemical-related neoplasms and nonneoplastic lesions were observed in the same sites as in the 2-year study: liver, large intestine, kidney, urinary bladder, and forestomach. After 9 months of dietary exposure to a concentration of 20,000 ppm 1-amino-2,4-dibromoanthraquinone, hepatocellular adenoma and carcinoma occurred in males and females. Nonneoplastic chemical-related lesions in the liver of exposed rats included pigmentation, focal hepatocellular alteration, and bile duct hyperplasia. Neoplasms at other sites in males included one adenomatous polyp (adenoma) in the large intestine and one transitional cell papilloma in the urinary bladder. Hyaline droplet accumulation was present in the kidney of exposed males at 9 months. In the stop-exposure groups examined at 15 months, hepatocellular adenoma and carcinoma were present in most males and females. Adenomatous polyp (adenoma) of the colon, renal tubule cell adenoma, and urinary bladder transitional cell papilloma and carcinoma also occurred in males and females. Nonneoplastic chemical-related lesions included foci of hepatocellular alteration in the liver and hyperplasia of the renal tubule epithelium and urinary bladder transitional epithelium. Hyperplasia, hyperkeratosis, inflammation, and ulceration were observed in the forestomach of some male and female rats continuously exposed for 15 months. 2-YEAR STUDY IN MICE: Groups of 60 male and 60 female mice were given 0, 10,000, or 20,000 ppm 1-amino-2,4-dibromoanthraquinone in feed for 104 weeks. The daily compound consumption was approximately 1,690 or 3,470 mg 1-amino-2,4-dibromoanthraquinone/kg body weight for males and 1,950 or 4,350 mg/kg for females. Ten animals from each group were evaluated for histopathology at 15 months. Survival, Body Weights, Feed Consumption, and Clinical Findings In the 2-year study, survival of exposed males was significantly lower than that of the controls. Survival of exposed females was similar to that of the controls. The final mean body weights of exposed males were 83% to 85% that of controls, and the final mean body weights of exposed females were 81% to 86% that of controls. Feed consumption by exposed groups was generally similar to that by controls. Discoloration of the fur, urine, and feces was observed in all exposed groups. Pathology Findings In the 2-year study, 1-amino-2,4-dibromoanthraquinone was associated with significant chemical-related increases in the incidences of benign and malignant neoplasms in the liver, forestomach, and lung of males and females. Incidences of hepatocellular adenoma and carcinoma were increased in exposed groups at the 15-month interim evaluation and at 2 years. At 2 years, there were significant increases in the incidences of multiple hepatocellular adenoma and carcinoma in males and females and in the incidences of hepatoblastoma in males. Centrilobular hypertrophy of hepatocytes in males and foci of hepatocellular alteration and pigmentation in the liver of males and females were also chemical-related changes. Sqamous cell papilloma of the forestomach mucosa occurred in 10,000 ppm females and 20,000 ppm males and females at the 15-month interim evaluation, and the incidences of squamous cell papilloma and carcinoma were significantly increased in exposed groups of males and females at 2 years. Chemical-related hyperplasia of forestomach epithelium was also present at 15 months and at 2 years. Alveolar/bronchiolar adenomas were present only in the exposed groups of males and females at 15 months, and the incidences of alveolar/bronchiolar adenoma were significantly increased in exposed males and females at 2 years. The incidences of multiple alveolar/bronchiolar adenomas were also increased in exposed males. In the kidney, pigmentation was present in the renal tubules of most mice after 2 years of exposure. DISPOSITION AND METABOLISM STUDIES: Adult male F344/N rats were given [14C]-labeled 1-amino-2,4-dibromoanthraquinone as a single intravenous dose of 0.4 mg/kg body weight or as a single oral dose of 2, 23, 118, 814, or 1,473 mg/kg. A 6-hour bile cannulation study was also performed. From day 0 through day 3 after intravenous administration, about 50% of the 14C was excreted in the feces, 15% in the urine, and 6% in expired air. Unmetabolized 1-amino-2,4-dibromoanthraquinone accounted for less than 3% of the excreted 14C after intravenous administration. For oral doses administered, the amount of the dose that was absorbed fit the equation: absorbed dose = 6.6 x log(dose). After intravenous administration, the metabolites of 1-amino-2,4-dibromoanthraquinone in blood were primarily in the plasma fraction (blood:plasma ratio of approximately 0.5:1). The highest concentrations of 14C in tissues 15 minutes after intravenous dosing were in excretory organs, lung, kidney, small intestine, liver, adipose tissue, and adrenal gland. GENETIC TOXICOLOGY: 1-Amino-2,4-dibromoanthraquinone was mutagenic in Salmonella typhimurium strains TA98 and TA1537 in the absence of S9; with S9, an equivocal response was observed in TA1537. 1-Amino-2,4-dibromoanthraquinone resulted in an equivocal response in TA100 with and without S9, and no mutagenic activity was detected with strain TA1535. In cultured Chinese hamster ovary cells, 1-amino-2,4-dibromoanthraquinone induced sister chromatid exchanges with and without S9; chromosomal aberrations were induced in the absence of S9. CONCLUSIONS: Under the conditions of these 2-year feed studies, there was clear evidence of carcinogenic activity of 1-amino-2,4-dibromoanthraquinone in male and female F344/N rats based on increased incidences of neoplasms in the liver, large intestine, kidney, and urinary bladder. There was clear evidence of carcinogenic activity of 1-amino-2,4-dibromoanthraquinone in male and female B6C3F1 mice based on increased incidences of neoplasms in the liver, forestomach, and lung. Exposure of male and female rats to 1-amino-2,4-dibromoanthraquinone for 2 years was associated with basophilic focus (males only), clear cell focus, eosinophilic focus, and pigmentation in the liver; renal tubule hyperplasia, renal tubule pigmentation, and transitional cell hyperplasia in the kidney; transitional cell hyperplasia, squamous metaplasia, and stromal metaplasia (females only) in the urinary bladder; squamous hyperplasia, hyperkeratosis, ulceration, and inflammation of the forestomach mucosa; and seminal vesicle atrophy. Exposure of male and female mice to 1-amino-2,4-dibromoanthraquinone for 2 years was associated with centrilobular hepatocellular hypertrophy (males only), basophilic focus, clear cell focus (females only), eosinophilic focus, and pigmentation in the liver; pigmentation in the kidney; and hyperplasia, basal cell hyperplasia, hyperkeratosis, and inflammation of the forestomach mucosa. Synonym: ADBAQ

Journal Article↗

NTP Initiation/Promotion Study of o-Benzyl-p-Chlorophenol (CAS No. 120-32-1) in Swiss (CD-1(R)) Mice (Mouse Skin Study).

o-Benzyl-p-chlorophenol (BCP), an aryl halide, is a broad spectrum germicide used in disinfectant solutions and soap formulations in United States hospitals and households. Human exposure to BCP occurs by absorption through the skin and mucous membranes and by ingestion. BCP was studied because of the widespread human exposure and because BCP is an irritant and certain phenolic compounds are weak promoters of skin neoplasia. Groups of Swiss (CD-1(R)) mice were used to study BCP in a 1-year mouse skin initiation/promotion protocol. Genetic toxicology studies were conducted in Salmonella typhimurium and cultured Chinese hamster ovary cells. 1-YEAR INITIATION/PROMOTION STUDY: Groups of 50 male and 50 female Swiss (CD-1(R)) mice were topically exposed to BCP to study its effect as an initiator, promoter, and complete carcinogen. A number of control groups were included in these studies as a reference for the responses of the mouse skin to o -benzyl- p -chlorophenol (see following table). See report abstract or full report for Dose Regimen for Reference Controls in the 1-Year Initiation/Promotion Study of o -Benzyl- p - Chlorophenol. BCP in acetone was tested as an initiator with the promoter 12- O -tetradecanoylphorbol-13-acetate (TPA). The potential of BCP as an initiator was studied by applying a single 100 mL dose of BCP in acetone at a concentration of 10 mg/mL to the dorsal interscapular region of the backs of mice during week 1 of the study. Following the initial BCP application, mice were administered promoting doses of 5 mg TPA three times per week in 100 mL acetone for the first 6 months of the study and once weekly for the final 6 months of the study. BCP in acetone was tested as a promoter with the initiator 7,12-dimethylbenz(a)anthracene (DMBA). Mice were administered a single initiating dose of 50 mL DMBA in 100 mL acetone. Beginning on the second week of the study, mice received 100 mL applications of 0.1, 1.0, or 3.0 mg BCP in acetone three times weekly for up to 51 weeks. Comparative control groups used during the study of BCP as a promoter included: vehicle control (acetone/acetone); promoter control (TPA/TPA); and initiator control (DMBA/acetone). The potential for BCP to act as a complete carcinogen was studied by applying a single initiating dose of 10 mg BCP in 100 mL of acetone, followed by tri-weekly 100 mL applications of 0.1, 1.0, or 3.0 mg BCP to 50 male and 50 female Swiss (CD-1(R)) mice for 52 weeks. The responses of these groups were compared to vehicle control (acetone/acetone) and complete carcinogen control (acetone/DMBA) groups. The following table shows the various groups with BCP as a promoter, an initiator, and as a complete carcinogen. See full report or abstract for Dose Regimen in the 1-Year Initiation/Promotion Study of o - Benzyl- p -Chlorophenol. Results in the Study of BCP as a Complete Carcinogen: BCP acted as an irritant when tested as a complete carcinogen using a single initiating dose of 10 mg BCP followed by repetitive applications of 0.1, 1.0, or 3.0 mg BCP for up to 52 weeks, and many of the mice developed cutaneous lesions of scaling/crusts and ulceration. During the course of the study, a single papilloma was first observed after 12 weeks in one 0.1 mg BCP male mouse. One 3.0 mg BCP female was observed with a papilloma at week 10, and three 0.1 mg BCP females were observed with papillomas between weeks 22 and 27. No mice administered BCP/BCP had papillomas at the end of the study, and no malignant cutaneous epithelial tumors were observed at the application sites on any BCP/BCP mice. Thus, in the present study, BCP was not a complete carcinogen. Results in the Study of BCP as an Initiator: One vehicle control (acetone/acetone) male mouse had developed crusts at the site of application at necropsy, but no male or female vehicle controls had developed papillomas. Mice administered BCP/TPA developed application site lesions including scaling/crusts, ulceration, and irritation; the incidences of these lesions were similar to those in the initiator/promoter control (DMBA/TPA) /TPA) groups. After 22 weeks papillomas were observed in 12/50 male mice administered BCP/TPA. After 12 weeks papillomas were observed in 7/50 female mice administered BCP/TPA. However, the incidences of papillomas in mice administered BCP/TPA were lower than those in mice administered TPA/TPA (males, 16/50; females, 16/50) and were much lower than those in DMBA/TPA mice (males, 40/50; females, 48/50). Although the incidences of papillomas in mice administered BCP as an initiator were significantly greater than those in the vehicle controls, the incidences were not significantly different from those in TPA/TPA mice. Thus, in the present study, BCP did not demonstrate initiating potential. Results in the Study of BCP as a Promoter: During the course of the study, incidences of scaling and/or crusts, ulceration, and irritation were observed at the site of application in DMBA/BCP male and female mice, and the incidences were dose-related. Incidences of scaling and/or crusts, ulceration, and irritation in 3.0 mg BCP mice were similar to the incidences of these lesions in initiator/promoter control (DMBA/TPA) group, but much higher than the incidences of these lesions in the initiator control (DMBA/acetone) group. A dose-related increased incidence of papillomas was observed in males (DMBA/acetone, 8/50; DMBA/0.1 mg BCP, 3/50;DMBA/1.0 mg BCP, 5/50; and DMBA/3.0 mg BCP, 14/50) and females (2/50, 6/50, 6/50, and 18/50). The incidence of papillomas in DMBA/3.0 mg BCP females was significantly greater (P<0.001) than that in DMBA/acetone females; the incidence of papillomas in DMBA/3.0 mg BCP males was marginally increased (P=0.077). No acetone/acetone mice developed papillomas. Although a higher percentage of DMBA/3.0 mg BCP mice developed papillomas over the course of the study than did DMBA/acetone controls, the time it took for half of the number of responding animals to develop papillomas was similar between DMBA/acetone groups and DMBA/3.0 mg BCP groups (DMBA/acetone males, week 38; DMBA/acetone females, week 34; DMBA/3.0 mg BCP males, week 36; DMBA/3.0 mg BCP females, week 37). However, the time to appearance of the first papilloma was shorter in DMBA/3.0 mg BCP mice (males, week 18; females, week 10) than in DMBA/acetone mice (males, week 26; females, week 27). BCP was considered to have promotion potential because the incidences of papillomas in mice treated with DMBA/3.0 mg BCP were greater than those in DMBA/acetone (initiator control) mice and because topical exposure to BCP alone caused no significant increased incidence of papillomas. However, the incidences of papillomas in DMBA/3.0 mg BCP mice (males, 14/50; females, 18/50) were much less than the incidences in DMBA/TPA (promoter control) mice (males, 40/50; females, 48/50); thus, BCP was classified as a weak promoter. GENETIC TOXICOLOGY: o -Benzyl- p -chlorophenol did not induce gene mutations in Salmonella typhimurium strains TA98, TA100, TA1535, or TA1537, and it did not induce sister chromatid exchanges or chromosomal aberrations in cultured Chinese hamster ovary cells. All tests were performed with and without S9 activation. CONCLUSIONS: Under the conditions of this 1-year mouse skin initiation/promotion study in Swiss (CD-1&reg;) mice, o -benzyl- p -chlorophenol was a cutaneous irritant and a weak skin tumor promoter relative to strong promoters such as TPA. BCP had no activity as an initiator or as a complete carcinogen.

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of Methylphenidate Hydrochloride (CAS No. 298-59-9) in F344/N Rats and B6C3F1 Mice (Feed Studies).

Methylphenidate hydrochloride is a drug used in the treatment of narcolepsy and attention deficit hyperactivity disorders. This drug was nominated for study by the Food and Drug Administration and the National Cancer Institute because of its widespread use in human medicine and because of lack of data on its potential carcinogenicity. Oral administration is the most common route of human exposure. Toxicology and carcinogenicity studies were conducted by administering methylphenidate hydrochloride (USP grade) ad libitum in feed to groups of male and female F344/N rats and B6C3F1, mice for 14 days, 13 weeks, or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium and in cultured Chinese hamster ovary cells. 14-DAY STUDY IN RATS: Groups of five male and five female F344/N rats were fed diets containing 0, 16, 62, 250, 1,000, or 4,000 ppm methylphenidate hydrochloride for 14 days. All rats survived to the end of the study. The final mean body weights of 4,000 ppm male and female rats were 9% lower than those of the controls. Absolute and relative liver weights of 4,000 ppm males and females were significantly greater than those of the controls. Clinical findings during the first week of the study included hyperactivity in 4,000 ppm males and females, but these animals appeared to be normal during the second week of treatment. No treatment-related gross lesions were observed; however, centrilobular hypertrophy was observed in 4,000 ppm males and females. 14-DAY STUDY IN MICE: Groups of five male and five female B6C3F1, mice were fed diets containing 0, 16, 62, 250, 1,000, or 4,000 ppm methylphenidate hydrochloride for 14 days. Three 4,000 ppm males died during the second week of the study; all other mice survived to the end of the study. The final mean body weight of 4,000 ppm females was 11% lower than that of the controls, and the mean body weight gains of 1,000 and 4,000 ppm males and females were also significantly lower than those of the controls. Absolute and relative liver weights of all exposed groups of males and of 4,000 ppm females were significantly greater than those of the controls. Hyperactivity was observed during the second week of the study in some 4,000 ppm males. Degeneration and necrosis of the renal tubule epithelium were observed in two 4,000 ppm males. Hepatocellular hypertrophy was observed in males and females exposed to 1,000 or 4,000 ppm and in males exposed to 250 ppm. 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female F344/N rats were fed diets containing 0, 125, 250, 500, 1,000, or 2,000 ppm methylphenidate hydrochloride for 13 weeks. There were no chemical-related effects on survival. Mean body weight gains of 500, 1,000, and 2,000 ppm males and females and of 250 ppm females were significantly lower than those of the controls. Final mean body weights of exposed males and females were similar to those of the controls. During the first week of the study, feed consumption by 2,000 ppm rats was less than that by controls, but during the remainder of the study feed consumption by exposed and control groups was similar. Rats exposed to 125, 250, 500, 1,000, or 2,000 ppm received approximate doses of 8, 15, 30, 70, or 130 mg methylphenidate hydrochloride per kilogram body weight per day (males) or 9, 18, 30, 70, or 150 mg/kg per day (females). Clinical findings in 1,000 and 2,000 ppm females included slight hypersensitivity to touch, hyperactivity, and increased vocalization during handling periods. Absolute and relative liver weights of 2,000 ppm males and females were significantly greater than those of the controls, as were the relative liver weights of 1,000 ppm males and females. No chemical-related differences in bone length, bone density, or nose-to-rump lengths were noted in males or females, nor were there treatment related histopathologic lesions. 13-WEEK STUDY IN MICE: Groups of 10 male and 10 female B6C3F1, mice were fed diets containing 0, 125, 250, 500, 1,000, or 2,000 ppm methylphenidate hydrochloride for 13 weeks. There were no chemical-related effects on ed effects on survival. Final mean body weights of males exposed to 250, 500, 1,000, or 2,000 ppm and of 2,000 ppm females were significantly lower than those of the controls. The final mean body weights of other exposed male and female groups were similar to those of the controls. During the first week of the study, feed consumption by 2,000 ppm mice was less than that by controls; feed consumption by exposed groups was similar to that by the controls throughout the remainder of the study. Mice exposed to 125, 250, 500, 1,000, or 2,000 ppm received approximate doses of 15, 30, 70, 115, or 230 mg/kg per day (males) or 15, 30, 70, 125, or 260 mg/kg per day (females). No chemical-related clinical findings were observed. Absolute and relative liver weights of 1,000 and 2,000 ppm males and females were significantly greater than those of the controls, as were the relative liver weights of 125, 250, and 500 ppm males. Centrilobular hypertrophy and hepatocellular degeneration or necrosis were observed in males exposed to 500, 1,000, or 2,000 ppm methylphenidate hydrochloride. 2-YEAR STUDY IN RATS: Based on the increased liver weights and lower body weight gains in 2,000 ppm rats in the 13-week study, the high dose selected for the 2-year rat study was 1,000 ppm. Groups of 70 male and 70 female F344/N rats were fed diets containing 0, 100, 500, or 1,000 ppm methylphenidate hydrochloride for up to 2 years. As many as 10 male and 10 female rats per exposure group were evaluated at 9 or 15 months. Survival, Body Weights, Feed and Compound Consumption, and Clinical Findings: Survival of exposed rats was similar to that of the controls at the end of the study. Mean body weights of 500 and 1,000 ppm males were 3&percnt; to 10&percnt; lower than those of the controls from week 30 to the end of the study; during the same time period, mean body weights of 500 and 1,000 ppm females were 4&percnt; to 24&percnt; less than those of the controls. Final mean body weights of rats exposed to 100, 500, or 1,000 ppm were 102&percnt;, 95&percnt;, or 90&percnt; (males) and 96&percnt;, 89&percnt;, or 78&percnt; (females) those of the controls. Rats exposed to 100, 500, or 1,000 ppm methylphenidate hydrochloride in feed received approximate doses of 5, 25, or 50 mg/kg per day (males and females). The only chemical-related clinical finding was an increased incidence of fighting among group-housed males exposed to 1,000 ppm. Hematology and Clinical Chemistry: No biologically significant differences in hematology or clinical chemistry parameters occurred at 9 or 15 months. Pathology Findings: In female rats exposed to 500 or 1,000 ppm, the incidence of mammary gland fibroadenomas was decreased (0 ppm, 15/49; 100 ppm, 13/50; 500 ppm, 6/ 48; 1,000 ppm, 5/50), and the decrease was considered to be related to chemical administration. No significant chemical-related increases in neoplasm incidences were observed in male or female rats. 2-YEAR STUDY IN MICE: Based on the liver toxicity and lower body weight gains observed in 1,000 and 2,000 ppm mice in the 13-week study, the high dose selected for the 2-year study was 500 ppm. Groups of 70 male and 70 female B6C3F1 mice were fed diets containing 0, 50, 250, or 500 ppm methylphenidate hydrochloride for 2 years. As many as 10 male and 10 female mice per exposure group were evaluated at 9 or 15 months. Survival, Body Weights, Feed and Compound Consumption, and Clinical Findings: Survival of exposed mice was similar to that of the controls at the end of the study. Mean body weights of mice exposed to 250 or 500 ppm were 3&percnt; to 11&percnt; lower than those of the controls throughout much of the study; during the same time period, mean body weights of 250 ppm females were 3&percnt; to 7&percnt; lower than those of the controls. Final mean body weights of mice exposed to 50, 250, or 500 ppm were 97&percnt;, 89&percnt;, or 93&percnt; (males) and 98&percnt;, 93&percnt;, or 97&percnt; (females) that of the controls. Mice exposed to 50, 250, or 500 ppm methylphenidate hydrochloride in feed were estimated to have received 6, 30, or 60 mg/kg body weight per day (males) or 8, 40, or 80 mg/kg per day (females). There were no chemical related clinical findings. Hematology and Clinical Chemistry: No biologically significant differences in hematology or clinical chemistry parameters occurred at 9 or 15 months. Pathology Findings: The principal lesions associated with the administration of methylphenidate hydrochloride occurred in the liver. A few hepatocellular neoplasms were observed in control and exposed male mice at the 9-and 15-month interim evaluations, but the incidences in exposed groups were not significantly increased. At the end of the 2-year study, incidences of eosinophilic foci were increased in 500 ppm males and females. Increased incidences of hepatoblastoma occurred in 500 ppm males (0 ppm, 0/50; 50 ppm, 1/50; 250 ppm, 1/50; 500 ppm, 5/50). Increased incidences of hepatocellular adenoma also occurred in 500 ppm males (18/50, 18/50, 16/50, 29/50) and females (6/49, 10/48, 10/49, 28/50). The incidences of hepatocellular carcinoma were similar among control and exposed mice. GENETIC TOXICOLOGY: Methylphenidate hydrochloride was not mutagenic in Salmonella typhimurium strains TA97, TA98, TA100, TA1535, or TA1537, with or without exogenous metabolic activation (S9). Methylphenidate hydrochloride was also tested for induction of sister chromatid exchanges and chromosomal aberrations in cultured Chinese hamster ovary cells. In the chromosomal aberrations tests, positive results were not consistently dependent upon the presence or absence of S9 activation. Sister chromatid exchanges were not increased in the presence of S9, but one laboratory did obtain a positive response without S9 by testing higher doses than were used in tests With S9. CONCLUSIONS: Under the conditions of these 2-year feed studies, there was no evidence of carcinogenic activity of methylphenidate hydrochloride in male or female F344/ N rats receiving 100, 500, or 1,000 ppm. There was some evidence of carcinogenic activity of methylphenidate hydrochloride in male and female B6C3F1 mice based on the occurrence of hepatocellular neoplasms. Treatment of female rats with methylphenidate hydrochloride was associated with a decrease in the incidence of mammary gland fibroadenomas. Administration of methylphenidate hydrochloride to male and female mice resulted in increased incidences of eosinophilic foci. Synonyms: a-phenyl-2-piperidineacetic acid methyl ester hydrochloride; methylphenidylacetate hydrochloride; a-phenyl-a-(2-piperidyl)acetic acid methyl ester hydrochloride; methyl a-phenyl-a-(2-piperidyl)acetate hydrochloride

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NTP Toxicology and Carcinogenesis Studies of Benzethonium Chloride (CAS No. 121-54-0) in F344/N Rats and B6C3F1 Mice (Dermal Studies).

Benzethonium chloride is used primarily in cosmetics for its antimicrobial and cationic surfactant properties. Benzethonium chloride was nominated by the National Cancer Institute to the NTP for study from a class study of chemicals used as biocides. The chemical was selected based on a suspicion of carcinogenicity and its known widespread human exposure. Male and female F344/N rats and B6C3F1 mice were topically administered benzethonium chloride (greater than 98% pure) for 16 days, 13 weeks, or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium and cultured Chinese hamster ovary cells. 16-DAY STUDY IN RATS: Groups of five male and five female F344/N rats were topically administered 0, 6.3, 12.5, 25, 50, or 100 mg benzethonium chloride/kg body weight. Rats were administered a total of 12 doses in a fixed volume of 250 &mgr;L ethanol. All rats survived to the end of the study. The final mean body weights and body weight gains of rats administered 50 or 100 mg benzethonium chloride/kg body weight were significantly less than those of the controls. Clinical findings at necropsy included thickening or hardening of the skin at the site of application in all rats administered 50 or 100 mg/kg and in 25 mg/kg males. Lesions at the site of application appeared crusty or red-grey in color. Epithelial hyperplasia with or without inflammation occurred at the site of application in all groups of males and females administered benzethonium chloride. 16-DAY STUDY IN MICE: Groups of five male and five female B6C3F1 mice were topically administered 0, 6.3, 12.5, 25, 50, or 100 mg benzethonium chloride/kg body weight. Mice were administered a total of 12 doses in a fixed volume of 100 &mgr;L ethanol. One 100 mg/kg male mouse died on day 4 of the study. Final mean body weights of all groups of males and females were similar to those of the controls. Clinical findings included mild irritation at the site of application in 50 and 100 mg/kg males and females and in 25 mg/kg males. Epithelial hyperplasia with or without inflammation occurred at the site of application in all groups of males and females administered benzethonium chloride. 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female F344/N rats were topically administered 0, 1.56, 3.13, 6.25, 12.5, or 25 mg benzethonium chloride/kg body weight, 5 days per week for 13 weeks. Doses were administered in ethanol at a volume not exceeding 300 &mgr;L. All rats survived to the end of the study. The final mean body weight and body weight gain of 25 mg/kg males were significantly lower than those of the controls. The final mean body weights of all other groups of males and of all groups of females were similar to those of the controls. Clinical findings included irritation at the site of application in groups administered 3.13 mg/kg or greater. There were no differences in absolute or relative organ weights considered to be related to chemical administration. Epithelial hyperplasia was observed at the site of application in all groups of males and females administered benzethonium chloride. Additionally, inflammation and ulceration were observed at the site of application in males and females administered 3.13 mg/kg or greater. Based on the lesions observed in the 13-week study, benzethonium chloride dose levels selected for the 2-year dermal study in male and female rats were 0.15, 0.5, and 1.5 mg/kg. 13-WEEK STUDY IN MICE: Groups of 10 male and 10 female B6C3F1 mice were topically administered 0, 1.56, 3.13, 6.25, 12.5, or 25 mg benzethonium chloride/kg body weight, 5 days per week for 13 weeks. Doses were administered in ethanol at a volume not exceeding 100 &mgr;L. All mice survived to the end of the study. The final mean body weights of all dosed groups of males and females were similar to those of the controls; the mean body weight gain of 25 mg/kg males was significantly less than that of the controls. Males administered 6.25, 12.5, or 25 mg/kg developed irritation, thickening of the skin, scales, and/or discoloration at the site of application, as did femaleale mice administered 12.5 or 25 mg/kg. Increased incidences of epithelial hyperplasia and inflammation were observed at the site of application in all groups of males and females administered benzethonium chloride. Based on the lesions observed in the 13-week study, benzethonium chloride dose levels selected for the 2-year dermal study in mice were 0.15, 0.5, and 1.5 mg/kg. 2-YEAR STUDY IN RATS: Groups of 60 male and 60 female F344/N rats were topically administered 0, 0.15, 0.5, or 1.5 mg benzethonium chloride/kg body weight 5 days per week for 103 weeks. Doses were administered in ethanol, and dose volumes were adjusted weekly according to the average body weights of the groups. As many as nine rats per group were evaluated after 15 months of chemical administration. Survival, Body Weights, and Clinical Findings: Survival of dosed rats was similar to that of the controls throughout the study. Mean body weights of all dosed groups of males and females were similar to those of the controls throughout the study. Reddening of the skin was observed at the site of application in all dosed groups of males and females. There were no other clinical findings considered to be related to chemical administration. Pathology Findings: There were no increased incidences of neoplasms in dosed male or female rats that were attributed directly to the administration of benzethonium chloride. Increased incidences of epithelial hyperplasia, sebaceous gland hyperplasia, and ulcers were observed at the site of application in dosed females. The incidence of epithelial hyperplasia was increased in 0.5 and 1.5 mg/kg males. 2-YEAR STUDY IN MICE: Groups of 60 male and 60 female B6C3F1 mice were topically administered 0, 0.15, 0.5, or 1.5 mg benzethonium chloride/kg body weight 5 days per week for 103 weeks. Doses were administered in ethanol, and dose volumes were adjusted weekly according to the average body weights of the groups. As many as 10 mice per group were evaluated after 15 months of chemical administration. Survival, Body Weights, and Clinical Findings: Survival of dosed mice was similar to that of the controls throughout the study. Mean body weights of all dosed groups of males and females were similar to those of the controls throughout the study. Reddening of the skin was observed at the site of application in all dosed groups of males and in 0.15 mg/kg females. There were no other clinical findings attributed to chemical administration. Pathology Findings: There were no increased incidences of neoplasms in dosed males or females that were related to administration of benzethonium chloride. Increased incidences of epithelial hyperplasia were observed at the site of application in dosed males and females. GENETIC TOXICOLOGY: Benzethonium chloride was not mutagenic in Salmonella typhimurium strains TA98, TA100, TA1535, or TA1537 and did not induce sister chromatid exchanges or chromosomal aberrations in cultured Chinese hamster ovary cells. All tests were conducted with and without S9 metabolic activation enzymes. CONCLUSIONS: Under the conditions of these 2-year dermal studies, there was no evidence of carcinogenic activity of benzethonium chloride in male or female F344/N rats receiving 0.15, 0.5, or 1.5 mg/kg. There was no evidence of carcinogenic activity in male or female B6C3F1 mice receiving 0.15, 0.5, or 1.5 mg/kg. Exposure of rats and mice to benzethonium chloride by dermal application in ethanol for 2 years resulted in epithelial hyperplasia in male and female rats and mice and sebaceous gland hyperplasia and ulcers in female rats at the site of application. Synonyms: Benzyldimethyl- p -(1,1,3,3-tetramethylbutyl) phenoxyethoxy-ethylammonium chloride; diisobutylphenoxyethoxyethyldimethyl benzyl ammonium chloride; p -tert-octylphenoxyethoxyethyldimethylbenzyl ammonium chloride Trade names: Anti-germ 77, Antiseptol, BZT, Diapp, Disilyn, Hyamine, Hyamine 1622, Phemeride, Phemithyn, Polymine D, Quatrachlor, Solamine

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of t -Butyl Alcohol (CAS No. 75-65-0) in F344/N Rats and B6C3F1 Mice (Drinking Water Studies).

t -Butyl alcohol is widely used in the manufacture of perfumes and a variety of cosmetics. It is also used as a raw material in the production of isobutylene, which may be used to produce methyl tertiary butyl ether, a common gasoline additive, or to produce butyl elastomers used in the production of automobile tires. Male and female F344/N rats and B6C3F1 mice were given t -butyl alcohol (greater than 99% pure) in drinking water for 13 weeks or 2 years. The genetic toxicity of t -butyl alcohol was assessed by testing the ability of the chemical to induce mutations in various strains of Salmonella typhimurium and in L5178Y mouse lymphoma cells, sister chromatid exchanges and chromosomal aberrations in cultured Chinese hamster ovary cells, and by measuring the frequency of micronucleated erythrocytes in mouse peripheral blood. 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female F344/N rats were given 0, 2.5, 5, 10, 20, or 40 mg/mL t -butyl alcohol in drinking water for 13 weeks. All males and six females given 40 mg/mL died during the study. Final mean body weights of 10 and 20 mg/mL males and of 40 mg/mL females were 12%, 17%, or 21% less than those of the corresponding controls, respectively. Serum sorbitol dehydrogenase activities in 10 and 20 mg/mL males were greater than that in the controls after 13 weeks. Serum alanine aminotransferase activity in 40 mg/mL females was greater than that in the controls after 2 weeks and greater in all exposed females after 13 weeks. Urine volumes of 10, 20, and 40 mg/mL males and females decreased, and urine specific gravity values increased. Transitional epithelial hyperplasia and inflammation of the urinary bladder were observed in 20 and 40 mg/mL males and 40 mg/mL females. Absolute and relative liver weights of all exposed groups of females and relative liver weights of 5, 10, and 20 mg/mL males were significantly greater than those of the controls. Absolute and relative kidney weights of all exposed groups of males and females were significantly greater than those of the controls. Incidences of mineralization of the kidney were significantly increased in 10, 20, and 40 mg/mL males. The severity of nephropathy in 2.5, 5, 10, and 20 mg/mL males was significantly greater than that of the controls as was the accumulation of hyaline droplets in the kidney of 5, 10, and 20 mg/mL males. The incidences of nephropathy in 10, 20, and 40 mg/mL females were significantly greater than that of the controls. 13-WEEK STUDY IN MICE: Groups of 10 male and 10 female B6C3F1 mice were given 0, 2.5, 5, 10, 20, or 40 mg/mL t -butyl alcohol in drinking water for 13 weeks. The deaths of two males and one female in the 40 mg/mL group were attributed to exposure to t -butyl alcohol. The final mean body weights of 20 and 40 mg/mL males and 40 mg/mL females were significantly lower than those of the controls. There were no biologically significant differences in hematology parameters of exposed and control groups of mice. Transitional epithelial hyperplasia and inflammation were observed in the urinary bladder of 20 and 40 mg/mL males and 40 mg/mL females. 2-YEAR STUDY IN RATS: Groups of 60 F344/N rats were given 0, 1.25, 2.5, or 5 mg/mL t -butyl alcohol (males) or 0, 2.5, 5, or 10 mg/mL t -butyl alcohol (females) in drinking water for 2 years. These correspond to average daily doses of approximately 90, 200, or 420 mg t -butyl alcohol/kg body weight for males and approximately 180, 330, or 650 mg t -butyl alcohol/kg body weight for females. Ten rats per group were evaluated after 15 months of chemical administration. Survival, Body Weights, and Water Consumption: Survival rates of 5 mg/mL males and 10 mg/mL females were significantly lower than those of the controls. The final mean body weights of exposed groups of males were 15% to 24% lower than that of the controls, and the final mean body weight of 10 mg/mL females was 21% lower than that of the controls. Water consumption by males increased with dose; water consumption by females decreased with dose. Hematology and Urinalysis: At the 15-month inte. Hematology and Urinalysis: At the 15-month interim evaluation, there were no significant differences in hematology parameters in males and females, and there were no significant differences in urinalysis parameters in males. Females given 5 or 10 mg/mL had increased urine specific gravities and decreased urine volumes. Pathology Findings: At the 15-month interim evaluation, relative kidney weights of 2.5 and 5 mg/mL males and absolute and relative kidney weights of 2.5, 5, and 10 mg/mL females were significantly greater than those of the controls. At 2 years, the incidence of mineralization in the kidney increased with dose and that of 5 mg/mL males was significantly greater than that of the controls. In the standard evaluation at the end of the study, the incidences of focal renal tubule hyperplasia and of adenoma were increased in exposed males and a carcinoma was observed in one 5 mg/mL male. Renal tubule hyperplasia occurred in one 10 mg/mL female. An extended evaluation of the kidney identified additional male rats with hyperplasia (control, 11/50; 1.25 mg/mL, 13/50; 2.5 mg/mL, 11/50; 5 mg/mL, 19/50) and renal tubule adenoma (7/50, 8/50, 15/50, 10/50); renal tubule carcinomas were identified in two 1.25 mg/mL males and in one 2.5 mg/mL male. Renal tubule adenoma was identified in one 5 mg/mL male from the 15-month extended evaluation. In the standard and extended evaluations combined, there were dose-related increased incidences of hyperplasia and adenoma. The severity of nephropathy and the incidence and severity of transitional cell hyperplasia of the kidney were increased in exposed male and female rats. Linear foci of mineralization were present in the renal papilla of exposed males. 2-YEAR STUDY IN MICE: Groups of 60 male and 60 female B6C3F1 mice were given 0, 5, 10, or 20 mg/mL t -butyl alcohol in drinking water for 2 years. Exposure levels of 5, 10, or 20 mg/mL delivered average daily doses of approximately 540, 1,040, or 2,070 mg t -butyl alcohol/kg body weight to males and approximately 510, 1,020, or 2,110 mg/kg to females. Survival, Body Weights, and Water Consumption: Survival of 20 mg/mL males was significantly lower than that of the controls. The final mean body weights of exposed groups of males were similar to those of the controls. The mean body weights of females given 20 mg/mL were 10&percnt; to 15&percnt; lower than those of the controls from week 13 to the end of the study. Water consumption by exposed groups of males and females was similar to that by the controls. Pathology Findings: Incidences of thyroid gland follicular cell hyperplasia were significantly increased in all exposed groups of males and in 10 and 20 mg/mL females. The incidence of follicular cell adenoma or carcinoma (combined) was marginally increased in 10 mg/mL males (0 mg/mL, 1/60; 5 mg/mL, 0/59; 10 mg/mL, 4/59; 20 mg/mL, 2/57). The incidence of follicular cell adenoma was significantly increased in 20 mg/mL females (2/58, 3/60, 2/59, 9/59). The incidences of chronic inflammation and transitional epithelial hyperplasia of the urinary bladder were increased in 20 mg/mL males and to a lesser extent in 20 mg/mL females. GENETIC TOXICOLOGY: t -Butyl alcohol was tested for induction of genetic damage in vitro and in vivo, and all results were negative. In vitro, t -butyl alcohol was negative in Salmonella typhimurium and mouse lymphoma cell mutation tests, and it did not induce sister chromatid exchanges or chromosomal aberrations in cultured Chinese hamster ovary cells. These in vitro studies were conducted with and without metabolic activation (S9). In vivo, no increase in micronucleated erythrocytes was observed in peripheral blood samples from mice administered t -butyl alcohol in drinking water for 13 weeks. CONCLUSIONS: Under the conditions of these 2-year drinking water studies, there was some evidence of carcinogenic activity of t -butyl alcohol in male F344/N rats based on increased incidences of renal tubule adenoma or carcinoma (combined). There was no evidence of carcinogenic activity in female F344/N rats receiving 2.5, 5, or 10 mg/mL t -butyl alcohol. There was equivocal evidence of carcinogenic activity of t -butyl alcohol in male B6C3F1 mice based on the marginally increased incidences of follicular cell adenoma or carcinoma (combined) of the thyroid gland. There was some evidence of carcinogenic activity of t -butyl alcohol in female B6C3F1 mice based on increased incidences of follicular cell adenoma of the thyroid gland. Exposure to t -butyl alcohol was associated with mineralization and renal tubule hyperplasia in male rats, transitional epithelial hyperplasia and increased severity of nephropathy of the kidney in male and female rats, follicular cell hyperplasia of the thyroid gland in male and female mice, and chronic inflammation and hyperplasia of the urinary bladder in male mice and to a lesser extent in female mice. Synonyms: 2-Methyl-2-propanol, 2-methylpropan-2-ol, TBA, t -butanol, tertiary butyl alcohol, t -butyl hydroxide, trimethyl carbinol, trimethyl methanol

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of Diethylphthalate (CAS No. 84-66-2) in F344/N Rats and B6C3F1 Mice (Dermal Studies) with Dermal Initiation/ Promotion Study of Diethylphthalate and Dimethylphthalate (CAS No. 131-11-3) in Male Swiss (CD-1(R)) Mice.

Diethylphthalate and dimethylphthalate are used as phthalate plasticizers, in an extensive array of products. The chronic dermal toxicity of diethylphthalate was evaluated in male and female F344/N rats and B6C3F1 mice in 2-year studies. In a series of special studies, the tumor initiation or promotion potential of diethylphthalate or dimethylphthalate was evaluated in male Swiss (CD-1(R)) mice by an initiation/promotion model of skin carcinogenesis. The genetic toxicity of diethylphthalate and dimethylphthalate in Salmonella typhimurium and cultured Chinese hamster ovary cells was also evaluated. 4-WEEK STUDY IN F344/N RATS: Groups of 10 male and 10 female rats were dermally administered diethylphthalate at volumes of 0, 37.5, 75, 150, or 300 &mgr;L (0, 46, 92, 184, or 369 &mgr;g) applied neat, 5 days per week for 4 weeks. All male and female rats survived to the end of the study. No evidence of dermatotoxicity was observed, with no adverse clinical signs observed and no effects on weight gain or feed consumption. Relative liver weights of 300 &mgr;L males and females and 150 &mgr;L females were greater than those of controls. Relative kidney weights of 150 and 300 &mgr;L males and 150 &mgr;L females were greater than those of controls. No other adverse effects were observed in this study. 4-WEEK STUDY IN B6C3F1 MICE: Groups of 10 male and 10 female mice were dermally administered diethylphthalate at volumes of 0, 12.5, 25, 50, or 100 &mgr;L (0, 15, 31, 62, or 123 &mgr;) applied neat, five days per week for 4 weeks. One control female died before the end of the study; all other mice survived. No evidence of dermatotoxicity or other adverse clinical signs were observed, and no clear adverse effects on weight gain or feed consumption were seen. Absolute and relative liver weights of 25 and 100 &mgr;L females were greater than those of the controls. Based on these 4-week study results, doses of 0, 35, and 100 &mgr;L diethylphthalate were recommended for the 2-year mouse studies. A chronic study in male and female B6C3F1 mice at 0, 35, and 100 &mgr;L (applied neat, once per day, 5 days per week) was started and subsequently stopped after 32 weeks when significant body weight reductions were noted in treated animals (males and females, 100 &mgr;L groups: 19% lower; males, 35 &mgr;L group: 12% lower; females, 35 &mgr;L group: 10% lower than controls). Based on these body weight reductions, doses of 0, 7.5, 15, and 30 &mgr;L in 100 &mgr;L acetone were recommended for the restart of the 2-year mouse study. 2-YEAR STUDY IN F344/N RATS: Based upon the results of the 4-week study, doses of 0, 100, or 300 &mgr;L diethylphthalate (0, 123, or 369 &mgr;) were chosen for the 2-year rat study. Groups of 60 male and 60 female rats received the doses applied neat 5 days per week for 103 weeks and up to 10 animals per group were evaluated after 15 months. Survival, Body Weights, and Clinical Findings: Survival of dosed rats during the first 15 months was similar to that of controls. However, 2-year survival was significantly reduced in all groups of male rats (survival probabilities, males: 0 &mgr;L, 8%; 100 &mgr;L, 12%; and 300 &mgr;L, 12%). The mean body weights of 300 &mgr;L males were slightly less than those of the controls throughout the study. No adverse clinical signs were observed, including no evidence of dermatotoxicity. Pathology Findings: No morphological evidence of dermal or systemic toxicity was observed in male or female rats. Skin neoplasms were not observed in female rats and were only rarely observed in male rats. A high incidence of anterior pituitary adenoma occurred in all groups of male and female rats. The incidence of anterior pituitary adenomas in the 0, 100, and 300 &mgr;L groups were: males, 39/44, 41/49, 41/49; females, 38/50, 33/49, 33/48. The incidence of this benign tumor in control males (84%) exceeded the historical control mean incidence [feed controls, (28.7%)] and range (12% to 60%). Anterior pituitary adenomas were considered a primary contributing factor in the increased mortality observed in all grtor in the increased mortality observed in all groups, regardless of treatment. A dose-related decreasing trend in the incidence of mammary gland fibroadenomas was observed in female rats (21/50, 12/48, 7/50). The incidence of mononuclear cell leukemia in male rats in this study was lower than the historical incidence and may be attributable to the shortened life span of male rats. Similarly, the incidence of interstitial cell tumors of the testes was markedly decreased in all groups of males (4/50, 3/50, 8/50), relative to historical control rates (90.1&percnt;; range 74&percnt;-98&percnt;). The incidence of fatty liver degeneration was notably lower in dosed rats than in controls (males: 26/50, 8/50, 4/51; females: 23/50, 11/50, 3/50). 2-YEAR STUDY IN B6C3F1 MICE: Groups of 60 male and 60 female mice received doses of 0, 7.5, 15, or 30 &mu;L diethylphthalate (0, 9, 18, or 37 &mu;) in 100 &mu;L acetone 5 days per week for 103 weeks with a 1 week recovery period, and up to 10 animals per group were evaluated after 15 months. Survival, Body Weights, and Clinical Findings: Two-year survival of dosed mice was similar to that of controls: 43/50, 41/48, 46/50, and 43/50 (males), and 41/50, 38/51, 37/49, and 36/49 (females). Mean body weights of dosed male and female mice were similar to those of the controls throughout the study. No adverse clinical signs were observed in mice, including no gross evidence of dermatotoxicity. Feed consumption by male and female mice was similar to or up to 13% greater than that by controls. Pathology Findings: No morphological evidence of dermal toxicity was observed in male or female mice. No skin neoplasms were observed in dosed male mice. In female mice receiving 30 &mu;L, one squamous cell carcinoma and one basal cell carcinoma were seen at the site of application. An increased incidence of liver neoplasms was observed in dosed male and female mice. The incidence of hepatocellular adenoma or carcinoma (combined) in B6C3F1 mice in the 0, 7.5, 15, and 30 &mu;L groups were: (males) 9/50, 14/50, 14/50, and 18/50; (females) 7/50, 16/51, 19/50, and 12/50. The incidence of adenoma or carcinoma (combined) was increased in 30 &mu;L male mice and the incidences of adenoma and of adenoma or carcinoma (combined) were increased in 7.5 and 15 &mu;L females. A positive dose-related trend in the incidence of adenoma or carcinoma (combined) was also observed in male mice. The incidence of basophilic hepatic foci was increased in 15 &mu;L male mice (0/50, 1/50, 9/50, 3/50). The increased incidence of liver neoplasms in this study was considered equivocal because the incidence of hepatocellular neoplasms in control and dosed males was within the historical range and because there was no clear dose-response relationship in females. No other treatment-related findings were observed in this study. 1-YEAR INITIATION/PROMOTION STUDY IN MALE SWISS (CD-1&reg;) MICE: Groups of 50 male mice were dosed dermally with diethylphthalate or dimethylphthalate to study their effect as initiators and promoters. Diethylphthalate and dimethylphthalate were tested as initiators with and without the known skin tumor promoter 12-O-tetradecanoylphorbol-13-acetate (TPA). Diethyl phthalate and dimethylphthalate were tested as promoters with and without the known skin tumor initiator 7,12-dimethylbenzanthrancene (DMBA). Comparative control groups used during the study of diethylphthalate and dimethylphthalate included: vehicle control (acetone/acetone); initiation/promotion control (DMBA/TPA); initiator control (DMBA/acetone); and promoter control (acetone/TPA). Based on the incidence of skin neoplasms diagnosed histologically and the multiplicity of skin neoplasms, there was no suggestion that either diethylphthalate or dimethylphthalate was able to initiate skin carcinogenesis when chronically promoted by TPA. Further, there was no evidence that either diethylphthalate or dimethylphthalate was able to promote skin carcinogenesis in skin previously initiated with DMBA. High incidences of both squamous cell papillomas and squamous cell carcinomas occurred among the initiation/promotion control animals initiated with DMBA and promoted with TPA. All TPA-dosed groups had significantly greater incidences of dermal acanthosis, ulceration, exudation, and hyperkeratosis than controls. GENETIC TOXICOLOGY: Neither diethylphthalate (10-10,000 &mu;/plate) nor dimethylphthalate (33-6,666 &mu;/plate) induced gene mutations in Salmonella typhimurium strains TA98, TA100, TA1535, or TA1537, with or without rat and hamster liver S9. In cultured Chinese hamster ovary cells, both diethylphthalate and dimethylphthalate induced sister chromatid exchanges in the presence of S9. Neither induced sister chromatid exchanges in the absence of S9. Neither chemical induced chromosomal aberrations, with or without S9, in cultured Chinese hamster ovary cells. CONCLUSIONS: Under the conditions of these 2-year dermal studies, there was no evidence of carcinogenic activity of diethylphthalate in male or female F344/N rats receiving 100 or 300 &mu;L. The sensitivity of the male rat study was reduced due to low survival in all groups. There was equivocal evidence of carcinogenic activity of diethylphthalate in male and female B6C3F1 mice based on increased incidences of hepatocellular neoplasms, primarily adenomas. In an initiation/promotion model of skin carcinogenesis, there was no evidence of initiating activity of diethylphthalate or dimethylphthalate in male Swiss (CD-1&reg;) mice. Further, there was no evidence of promotion activity of diethylphthalate or dimethylphthalate in male Swiss (CD-1&reg;) mice. The promoting activity of TPA following DMBA initiation was confirmed in these studies. Minor dermal acanthosis was observed following dermal application of diethylphthalate in male and female F344/N rats dosed for 2 years and in male Swiss (CD-1&reg;) mice dosed for 1 year. Synonyms: Diethylphthalate (CAS No. 84-66-2): 1,2-benzenedicarboxylic acid, diethyl ester; DEP; diethyl 1,2-benzenedicarboxylate; diethyl o-phthalate; diethyl phthalate; ethyl phthalate; o-benzenedicarboxylic acid diethyl ester; phthalic acid, diethyl ester; RCRA U088 Dimethylphthalate (CAS No. 131-11-3): 1,2-benzenedicarboxylic acid, dimethyl ester; dimethyl 1,2-benzenedicarboxylate; dimethyl benzene-o-dicarboxylate; dimethyl benzeneorthodicarboxylate; dimethyl o-phthalate; dimethyl phthalate; DMP; FIFRA 028002; methyl phthalate; go-dimethyl phthalate; phthalic acid, dimethyl ester; phthalic acid methyl ester; RCRA U102

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of p-Nitrobenzoic Acid (CAS No. 62-23-7) in F344/N Rats and B6C3F1 Mice (Feed Studies).

p-Nitrobenzoic acid is produced in large volumes for organic synthesis and as an intermediate in the manufacture of pesticides, dyes, and industrial solvents. Groups of male and female F344/N rats and B6C3F1 mice were exposed to p-nitrobenzoic acid (>99% pure) in feed for 14 days, 13 weeks, or 2 years for toxicity and carcinogenicity studies. Genetic toxicology studies were conducted in in vitro assays with Salmonella typhimurium and cultured Chinese hamster ovary cells, and in studies of erythrocyte micronucleus formation in mice in the 13-week study. 14-DAY STUDY IN RATS: Groups of five male and five female rats were given 0, 2,500, 5,000, 10,000, 20,000, or 40,000 ppm p-nitrobenzoic acid in feed for 14 days. All rats survived until the end of the study. Male and female rats given 20,000 and 40,000 ppm lost weight. The final mean body weights of 10,000, 20,000, and 40,000 ppm males were 82%, 60%, or 52% that of the controls, and the final mean body weights of 10,000, 20,000, and 40,000 ppm females were 87%, 68%, and 65% that of the controls. There were no clinical findings that were characteristic of organ-specific toxicity. Absolute and relative spleen weights were significantly increased in rats exposed to 10,000, 20,000, and 40,000 ppm. There were decreases in erythrocyte count and hemoglobin and hematocrit values and increases in reticulocyte count, nucleated erythrocytes, and methemoglobin concentration that were most pronounced in the 20,000 and 40,000 ppm groups. Congestion of the spleen occurred in 10,000 ppm males and in 20,000 and 40,000 ppm females. Hypertrophy of the follicular epithelium of the thyroid gland was present in male and female rats exposed to 10,000, 20,000, or 40,000 ppm p-nitrobenzoic acid, while follicular hyperplasia was observed in the 40,000 ppm males and females. Atrophy of the testis was observed in 20,000 and 40,000 ppm males. Other lesions observed in 20,000 and 40,000 ppm rats included atrophy of the thymus in males and atrophy of the ovary, bone marrow, and thymus in females. 14-DAY STUDY IN MICE: Groups of five male and five female mice were given 0, 2,500, 5,000, 10,000, 20,000, or 40,000 ppm p-nitrobenzoic acid in feed for 14 days. Three males and two females given 40,000 ppm died during the study. All other animals survived until the end of the study. Male mice given 20,000 and 40,000 ppm and females given 20,000 ppm lost weight. Mean body weight gains of 20,000 and 40,000 ppm males and 10,000, 20,000, and 40,000 ppm females were significantly lower than those of the controls. There were no clinical findings related to organ-specific toxicity although lethargy and ataxia were observed in 40,000 ppm mice. Relative liver weights were significantly increased in 20,000 and 40,000 ppm males and females and in 10,000 ppm females. Absolute and relative thymus weights of 20,000 and 40,000 ppm males and of 10,000, 20,000, and 40,000 ppm females were reduced. No significant differences in hematology parameters occurred in exposed mice. Testicular degeneration was observed in three 20,000 ppm and two 40,000 ppm males. Bone marrow hemorrhage and atrophy occurred in 40,000 ppm females. 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female rats were given 0, 630, 1,250, 2,500, 5,000, or 10,000 ppm pnitrobenzoic acid in feed for 13 weeks resulting in approximate daily doses of 40, 70, 160, 310, or 660 mg/kg to males and 40, 80, 170, 340, or 680 mg/kg to females. All rats survived until the end of the study. Mean body weight gains and final mean body weights were significantly less than those of the controls in 2,500, 5,000, and 10,000 ppm males and in 5,000 and 10,000 ppm females. There were no clinical findings related to organ-specific toxicity. Differences in spleen weights and hematology parameters characteristic of regenerative anemia were observed in males and females, primarily in groups given 10,000 ppm. The absolute and relative spleen weights were significantly increased in 10,000 ppm males and females and the relative spleen weights were significantly increased in 5,000 ppm males hts were significantly increased in 5,000 ppm males and females. Methemoglobin, Heinz bodies, and reticulocyte counts were increased and erythrocyte counts, hemoglobin, and hematocrit values were decreased in 10,000 ppm males and females. Congestion, pigmentation, and accumulation of macrophages in the spleen and pigmentation in the kidney occurred in 2,500, 5,000, and 10,000 ppm males. Congestion and pigmentation of the spleen occurred in 10,000 ppm females. A yellowish brown pigment (hemosiderin) in the spleen and kidney was associated with hemolytic anemia. Mild cytoplasmic hyaline droplet accumulation was present in renal tubule epithelial cells in 10,000 ppm males while karyomegaly was present in male and female rats exposed to 2,500, 5,000, and 10,000 ppm p-nitrobenzoic acid. A chemical-related testicular lesion, consisting of atrophy of the seminiferous tubules, occurred in 10,000 ppm males. 13-WEEK STUDY IN MICE: Groups of 10 male and 10 female mice were given 0, 1,250, 5,000, 10,000, or 20,000 ppm pnitrobenzoic acid in feed for 13 weeks resulting in approximate daily doses of 170, 330, 670, 1,900, or 4,000 mg/kg body weight to males and 240, 460, 970, 2,500, or 4,900 mg/kg to females. All mice survived until the end of the study, except one 1,250 ppm female that was killed accidentally. Final mean body weights and mean body weight gains of all exposed males and of 5,000, 10,000, and 20,000 ppm females were significantly lower than those of the controls. No clinical findings or differences in organ weights or histopathology related to organ-specific toxicity were observed in exposed mice. 2-YEAR STUDY IN RATS: Groups of 60 male and 60 female rats were given 0, 1,250, 2,500, or 5,000 ppm p-nitrobenzoic acid in feed for 2 years. Ten males and 10 females from each exposure group were evaluated at 15 months. Survival, Body Weights, Feed Consumption, and Clinical Findings: Two-year survival rates of 1,250 and 2,500 ppm males were similar to that of the controls. Two-year survival of 5,000 ppm males was marginally greater than that of the controls and was attributed in part to a decrease in the severity of nephropathy and a decrease in the incidence of mononuclear cell leukemia. Survival of exposed females was similar to that of the controls. Mean body weights of 5,000 ppm males were 2&percnt; to 8&percnt; lower than those of the controls through week 80. Final mean body weights of exposed males were similar to that of the controls. Mean body weights of 5,000 ppm females were 2&percnt; to 9&percnt; lower than those of the controls during the first year of the study and were 10&percnt; to 16&percnt; lower during the second year of the study. Final mean body weights of exposed females were 97&percnt; (1,250 ppm), 92&percnt; (2;500 ppm), and 84&percnt; (5,000 ppm) that of the controls. Feed consumption by exposed males and females was similar to that by the controls. Dietary levels of 1,250, 2,500, or 5,000 ppm p-nitrobenzoic acid delivered approximately 50, 100, or 210 mg/kg body weight per day to males and 60, 125, or 250 mg/kg per day to females. There were no clinical findings attributable to organ-specific toxicity. Pathology Findings: There were increases in the incidences of clitoral gland adenoma and of clitoral gland adenoma or carcinoma (combined) (4/50, 14/49, 15/49, 15/50) in exposed females. The incidences of clitoral gland adenoma or carcinoma (combined) in the exposed groups (29&percnt; to 31&percnt;) exceeded the historical control mean incidence (11&percnt;) and range (2&percnt; to 21&percnt;) in female F344/N rats in recent 2-year NTP feed studies. The increased incidences of clitoral gland neoplasms were considered to be some evidence of carcinogenic activity in female rats exposed to p-nitrobenzoic acid. The incidences of hyperplasia of the clitoral gland in exposed females were marginally lower than that of the controls (10/50, 6/49, 6/ 49, 7/50). There was a chemical-related decrease in the severity of nephropathy in male rats. Male rat kidneys were examined using both single and step-section analyses, and the incidences of renal tubule neoplasms were not statistically greater than those of the controls. Mild hyaline droplet accumulation was observed in renal tubule epithelial cells in 10,000 ppm males in the 13-week study, but this effect was not severe enough to lead to a chemical-related neoplastic response in the 2-year study as has been observed with other chemicals. At the 15-month interim evaluation, hematologic parameters characteristic of a mild regenerative anemia and significant differences in spleen weights were noted in 5,000 ppm females. These differences included decreases in erythrocyte count, hemoglobin, and hematocrit, increases in spleen weights, and hemosiderin accumulation in splenic macrophages. At 2 years, significant decreases in the incidences of mononuclear cell leukemia were observed in 5,000 ppm males and 2,500 and 5,000 ppm females (males: 29/50, 35/50, 26/50, 2/50; females: 17/50, 11/50, 3/50, 0/50). While the mechanism for this decrease is unknown, decreases in the incidence of mononuclear cell leukemia have also been observed in 2year studies with other amine/nitro compounds. 2-YEAR STUDY IN MICE: Groups of 60 male and 60 female mice were given 0, 1,250, 2,500, or 5,000 ppm p-nitrobenzoic acid in feed for 2 years. Ten males and 10 females from each exposure group were evaluated at 15 months. Survival, Body Weights, Feed Consumption, and Clinical Findings: Two-year survival rates of exposed mice were similar to those of the controls. Mean body weights of 5,000 ppm males were 6&percnt; to 12&percnt; lower than those of the controls after week 17, and mean body weights of 5,000 ppm females were 12&percnt; to 24&percnt; lower than those of the controls after week 16. The final mean body weight of 5,000 ppm females was 19&percnt; less than that of the controls; final mean body weights of males were similar to that of the controls. Feed consumption by exposed mice was similar to that by the controls. Dietary levels of 1,250, 2,500, or 5,000 ppm p-nitrobenzoic acid delivered approximately 150, 300, or 675 mg/kg per day to males and 170, 365, or 905 mg/kg per day to females. There were no clinical findings of organ-specific toxicity. No chemical-related effects on hematology parameters were noted at the 15-month interim evaluation. Pathology Findings: There were no increases or decreases in neoplasms in male or female mice that were considered to be related to chemical administration. GENETIC TOXICOLOGY: p-Nitrobenzoic acid was mutagenic in Salmonella typhimurium strain TA100 with and without S9. No mutagenic activity was noted in strains TA98, TA1535, or TA1537, with or without S9. p-Nitrobenzoic acid induced sister chromatid exchanges and chromosomal aberrations in cultured Chinese hamster ovary cells in the absence of S9; with S9, results of both tests were negative. In vivo, no increase in micronuclei was observed in peripheral blood erythrocytes of male or female mice administered p-nitrobenzoic acid in dosed feed for 13 weeks. CONCLUSIONS: Under the conditions of these 2-year feed studies, there was no evidence of carcinogenic activity of p-nitrobenzoic acid in male F344/N rats exposed to 1,250, 2,500, or 5,000 ppm. There was some evidence of carcinogenic activity of p-nitrobenzoic acid in female F344/N rats based on increases in the incidences of clitoral gland adenoma and of clitoral gland adenoma or carcinoma (combined). There was no evidence of carcinogenic activity of p-nitrobenzoic acid in male or female B6C3F1 mice exposed to 1,250, 2,500, or 5,000 ppm. There were chemical-related decreases in the incidences of mononuclear cell leukemia in exposed male and female rats. p-Nitrobenzoic acid caused mild hematologic toxicity in female rats. Synonyms: 4-Nitrobenzoic acid; nitrodracylic acid; p-nitrobenzenecarboxylic acid; p-carboxynitrobenzene

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of Ozone (CAS No. 10028-15-6) and Ozone/NNK (CAS No. 10028-15-6/ 64091-91-4) in F344/N Rats and B6C3F1 Mice (Inhalation Studies).

There is widespread concern over the health effects of oxidant air pollutants. The state of California and the Health Effects Institute (HEI) (a nonprofit research institute funded jointly by the U.S. Environmental Protection Agency [USEPA] and combustion engine manufacturers) nominated ozone for evaluation in long-term animal studies. The NTP study designs were a result of a series of meetings at the NIEHS with scientists from NIEHS, USEPA, and HEI, as well as experts from academic institutions working in the area of air pollutants. Male and female F344/N rats and B6C3F1 mice were exposed to ozone by inhalation for 4 weeks, 2 years, or for 124 weeks (rats) or 130 weeks (mice). The oxygen used to generate the ozone was greater than 99.9% pure. Additional groups of male F344/N rats were administered injections of 4-(N-methyl-Nnitrosamino)-1-(3-pyridyl)-1-butanone (NNK) (~99% pure) 3 times per week for 20 weeks and exposed to ozone by inhalation for 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium. 4-WEEK OZONE STUDY IN RATS: Groups of five male and five female F344/N rats were exposed to 0, 0.5, or 1.0 ppm ozone by inhalation 6 hours per day, 5 days per week, for a total of 20 days. All rats survived to the end of the study. The final mean body weights and mean body weight gains of 0.5 ppm males and females and of 1.0 ppm females were similar to those of the controls. The final mean body weight of 1.0 ppm males was 7% lower than that of the controls. Clinical findings included hypoactivity in 1.0 ppm males and females and ruffled fur in exposed groups of males. Male and female rats exposed to 0.5 or 1.0 ppm developed multifocal lesions of the lung, which consisted of infiltration of granulocytes and macrophages with extension of the bronchial epithelium into the alveolar ducts. Female rats exposed to ozone developed minimal squamous metaplasia of the laryngeal epithelium at the base of the epiglottis. Absolute and relative lung weights of all exposed groups of males and females were greater than those of the controls, and absolute and relative thymus weights of all exposed groups were generally lower than those of the controls. 4-WEEK OZONE STUDY IN MICE: Groups of five male and five female B6C3F1 mice were exposed to 0, 0.5, or 1.0 ppm ozone by inhalation 6 hours per day, 5 days per week, for a total of 20 days. All mice survived to the end of the study. The final mean body weights and body weight gains of all exposed groups of mice were less than those of the controls. Hypoactivity was observed in 1.0 ppm mice. Male and female mice exposed to 0.5 or 1.0 ppm ozone developed patchy, multifocal lesions of the lung, which consisted of infiltration of granulocytes and macrophages with extension of the bronchial epithelium into the alveolar ducts. The relative lung weight of 1.0 ppm males was significantly greater than that of the controls. There were no other statistically significant differences in absolute or relative organ weights in males or females. 2-YEAR OZONE STUDY IN RATS: The 2-year study was designed to include the present USEPA standard (0.12 ppm), the maximum concentration believed compatible with long-term survival (1.0 ppm), and an intermediate concentration (0.5 ppm). Groups of 50 male and 50 female F344/N rats were exposed to 0, 0.12, 0.5, or 1.0 ppm ozone by inhalation for 6 hours per day, 5 days per week, for 105 weeks. Survival, Body Weights, and Clinical Findings: Survival of exposed groups of rats was similar to that of the controls at the end of the study. The mean body weights of 0.12 and 0.5 ppm males and females were similar to those of the controls throughout the study. The mean body weights of 1.0 ppm males and females were slightly lower than those of the controls throughout the study. Hypoactivity was observed in male and female rats exposed to ozone. Pathology Findings: Increased incidences of ozone-induced metaplasia occurred in the nose and lung of rats exposed to 0.5 or 1.0 ppm ozone. The lesions in the nose were characterized by an increase in the number of goblin the number of goblet cells in the respiratory epithelium with mild squamous metaplasia of the cuboidal epithelium on the lateral wall. The increase in the number of goblet cells was found primarily in level I and II epithelium occurring along the lateral wall and on the maxilloturbinates and nasoturbinates. The metaplasia in the lung was a patchy multifocal lesion consisting of extension of the bronchial epithelium into the alveoli of the centriacinar region. This may represent more an extension of the bronchial epithelium into the pulmonary parenchyma than an actual transition of one epithelial cell type into another. There were increased incidences of squamous metaplasia at the base of the epiglottis characterized by one or more layers of flattened epithelial cells where low cuboidal cells are normally found. There were no increases in the incidences of alveolar/bronchiolar adenoma or carcinoma in either males or females exposed to ozone. LIFETIME OZONE STUDY IN RATS: For this study, rats were exposed to 0.5 and 1.0 ppm ozone for an additional 6 months to determine the effect of extended exposure on neoplasm incidence. Groups of 50 male and 50 female F344/N rats were exposed to 0, 0.5, or 1.0 ppm ozone by inhalation for 6 hours per day, 5 days per week, for 125 weeks. Survival, Body Weights, and Clinical Findings: Survival rates of exposed rats were similar to those of the controls. The mean body weights of 0.5 ppm males and females were similar to those of the controls throughout the study. The mean body weights of 1.0 ppm males and females were slightly lower than those of the controls for the first two years of the study. Hypoactivity was observed in exposed groups of males and females. Pathology Findings: Increased incidences of metaplasia occurred in the nose, larynx, and lung of rats exposed to 0.5 or 1.0 ppm ozone. The lung lesions were multifocal, centriacinar and were characterized by the presence of cuboidal epithelium (ciliated and nonciliated) along the alveolar ducts where type I epithelium is normally present. Inflammation (histiocytic infiltration) and interstitial fibrosis were observed in the lung of exposed males and females, and hyperplasia was observed in the nose of exposed male and female groups. There were no ozone-related increased incidences of neoplasms. 2-YEAR OZONE/NNK STUDY IN MALE RATS: An intermediate concentration of 0.5 ppm ozone was combined with exposure to two levels of a known carcinogen (0.1 and 1.0 mg NNK/kg body weight) in order to determine if ozone promotes the carcinogenic process or acts as a cocarcinogen. Groups of 48 male F344/N rats were exposed to 0 or 0.5 ppm ozone by inhalation, 6 hours per day, 5 days per week for 105 weeks. During the first 20 weeks of the study, these rats were subcutaneously injected with 0, 0.1, or 1.0 mg NNK per kg body weight in trioctanoin three times weekly. Survival and Body Weights: Two-year survival rates of male rats were similar in all groups. Final mean body weights of all males exposed to NNK alone or NNK and ozone were similar to that of the controls, with the exception of rats exposed to 1.0 mg NNK/kg body weight and 0.5 ppm ozone. Hypoactivity was observed in males exposed to NNK and ozone, in those exposed to NNK without ozone, and in those exposed to ozone only. Pathology Findings: Alveolar epithelial metaplasia and interstitial fibrosis occurred in all groups of rats exposed to ozone or to NNK and ozone, but not in those exposed to NNK without ozone. Increased incidences of hyperplasia occurred in groups of rats exposed to NNK or to ozone and NNK. Incidences of hyperplasia were similar among groups of rats exposed to NNK only. An increased incidence of alveolar/bronchiolar adenoma or carcinoma (combined) occurred in rats administered 1.0 mg/kg NNK, with or without ozone. The administration of ozone did not affect the occurrence of pulmonary neoplasms or nonneoplastic lesions in rats administered NNK. 2-YEAR OZONE STUDY IN MICE: The 2-year study was designed to include the present USEPA standard (0.12 ppm), the maximum concentration believed compatible with long-term survival (1.0 ppm), and an intermediate concentration (0.5 ppm). Groups of 50 male and 50 female B6C3F1 mice were exposed to 0, 0.12, 0.5, or 1.0 ppm ozone by inhalation for 6 hours per day, 5 days per week, for 105 weeks. Survival, Body Weights, and Clinical Findings: Survival rates of exposed mice were generally similar to those of the controls; the 2-year survival rate of 1.0 ppm females was greater than that of the controls. The mean body weights of 0.12 and 0.5 ppm males were similar to that of the controls throughout the study; the mean body weights of 1.0 ppm males and of all exposed groups of females were generally lower than those of the controls throughout the study. Hypoactivity was observed in male and female mice exposed to ozone. Pathology Findings: Increased incidences of metaplasia occurred in the nose and lung of mice exposed to 0.5 or 1.0 ppm ozone. The metaplasia in the nose consisted of increased thickening and extension of the squamous epithelium in the anterior portion of the nasal passage. The metaplasia in the lung consisted of extension of the bronchial epithelium into the alveoli of the centriacinar region. There were increased incidences of hyperplasia in the nose characterized by thickening of the noncuboidal (transitional) epithelium. There were increased incidences of hyperplasia in the epiglottis of female mice, a change that was characterized by a minimal increase in the thickness of the epithelium. Incidences of alveolar/bronchiolar adenoma or carcinoma (combined) were marginally increased in 0.5 and 1.0 ppm males (0 ppm, 14/50; 0.12 ppm, 13/50; 0.5 ppm, 18/50; 1.0 ppm, 19/50) and were increased in 1.0 ppm females (6/50, 7/50, 9/49, 16/50). LIFETIME OZONE STUDY IN MICE: For this study, mice were exposed to 0.5 and 1.0 ppm ozone for 30 months to determine the effect of extended exposure on neoplasm incidence. Groups of 50 male and 50 female B6C3F1 mice were exposed to 0, 0.5, or 1.0 ppm ozone by inhalation for 6 hours per day, 5 days per week, for 130 weeks. Survival and Body Weights: Survival rates of exposed mice were similar to those of the controls. The mean body weights of 0.5 ppm males and females were similar to those of the controls throughout the study. The mean body weights of 1.0 ppm males and females were generally lower than those of the controls throughout the study. Hypoactivity was observed in male and female mice exposed to ozone. Pathology Findings: The incidences of alveolar/bronchiolar adenoma and carcinoma (combined) were marginally increased in exposed males (0 ppm, 16/49; 0.5 ppm, 22/49; 1.0 ppm, 21/50) and in exposed females (6/50, 8/49, 12/50). Increased incidences of metaplasia occurred in the nose, larynx, and lung of exposed groups of males and females, and the incidences of hyperplasia were increased in the larynx and nose of exposed mice. The morphology of the lesions was similar to that seen in the 2-year study. There were no ozone-related increases in alveolar epithelial hyperplasia. GENETIC TOXICOLOGY: Ozone was mutagenic in Salmonella typhimurium strain TA102, with and without S9 metabolic activation. CONCLUSIONS: Under the conditions of these 2-year and lifetime inhalation studies, there was no evidence of carcinogenic activity of ozone in male or female F344/N rats exposed to 0.12, 0.5, or 1.0 ppm. There was equivocal evidence of carcinogenic activity of ozone in male B6C3F1 mice based on increased incidences of alveolar/bronchiolar adenoma or carcinoma. There was some evidence of carcinogenic activity of ozone in female B6C3F1 mice based on increased incidences of alveolar/bronchiolar adenoma or carcinoma. There was no evidence that exposure to 0.5 ppm ozone enhanced the incidence of NNK-induced pulmonary neoplasms in male rats. Exposure of male and female rats to ozone for 2 years or 125 weeks was associated with goblet cell hyperplasia and squamous metaplasia in the nose, squamous metaplasia in the larynx, and metaplasia (extension of bronchial epithelium into the centriacinar alveolar ducts) and interstitial fibrosis in the lung. Exposure of male and female mice to ozone for 2 years or 130 weeks was associated with hyperplasia and squamous metaplasia in the nose and inflammation (histiocytic infiltration) and metaplasia (extension of bronchial epithelium into the centriacinar alveolar ducts) of the lung.

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of Hexachlorocyclopentadiene (CAS No. 77-47-4) in F344/N Rats and B6C3F1 Mice (Inhalation Studies).

Hexachlorocyclopentadiene is an intermediate used in the manufacture of flame retardants, resins, and chlorinated cyclodiene pesticides. Toxicology and carcinogenesis studies were conducted by exposing male and female F344/N rats and B6C3F1 mice to atmospheres containing hexachlorocyclopentadiene (approximately 98% pure) for 6 hours per day, 5 days per week, for 13 weeks or 2 years. A stop-exposure evaluation was conducted in male B6C3F1 mice to determine the influence of exposure level and exposure duration on the development of nonneoplastic lesions of the respiratory tract and on their regression or progression after exposure was stopped. Genetic toxicology studies were conducted in Salmonella typhimunum, cultured Chinese hamster ovary cells, Drosophila melanogaster, and mouse peripheral blood samples were analyzed for frequency of micronucleated normochromatic erythrocytes. 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female rats were exposed to atmospheres containing 0, 0.04, 0.15, 0.4, 1, or 2 ppm (equivalent to 0, 0.45, 1.67, 4.46, 11.14, and 22.28 mg/m(3)) hexachlorocyclopentadiene. Additional rats were exposed to 0, 0.04, 0.4, or 2 ppm hexachlorocyclopentadiene and evaluated for differences in clinical pathology parameters. All rats in the 1 and 2 ppm groups died during the first 4 weeks of the study. The final mean body weight and mean body weight gain of males exposed to 0.4 ppm were significantly lower than those of the controls. Listlessness was observed in 2 ppm rats from week 1, in 1 ppm rats from week 2, and in 0.4 ppm rats during week 3. Rats exposed to 1 or 2 ppm also experienced respiratory distress. No chemical-related differences in hematology, clinical chemistry, or urinalysis parameters were observed in male or female rats. Absolute and relative lung weights of 0.4 ppm males were significantly greater than those of the controls. Inflammation (necrotizing, chronic, or suppurative) of the nose, larynx, trachea, and lung was observed in 0.4, 1, and 2 ppm males and females. Squamous metaplasia of the epithelial lining of the nose of 0.4 ppm males and 1 and 2 ppm males and females was also observed. 13-WEEK STUDY IN MICE: Groups of 10 male and 10 female mice were exposed to atmospheres containing 0, 0.04, 0.15, 0.4, 1, or 2 ppm (equivalent to 0, 0.45, 1.67, 4.46, 11.14, and 22.28 mg/m(3)) hexachlorocyclopentadiene. Additional mice were exposed to 0, 0.04, 0.4, or 2 ppm and evaluated for differences in clinical pathology parameters. All 2 ppm mice died during the first week of exposure. All 1 ppm mice died during the first 5 weeks of exposure. Five males and two females in the 0.4 ppm group died during the first 2 weeks of exposure. Deaths in the other groups were not related to hexachlorocyclopentadiene exposure. Final mean body weights of males exposed to 0.15 and 0.4 ppm and the body weight gain of 0.4 ppm males were significantly lower than those of the controls. Treatment-related clinical findings included listlessness in 0.4 and 1 ppm males and females. No chemical-related differences in hematology, clinical chemistry, or urinalysis parameters were observed in male or female mice. Necrosis or inflammation of the nose, larynx, trachea, or lung occurred in mice exposed to 0.4,1, and 2 ppm hexachlorocyclopentadiene. Squamous metaplasia of the larynx or trachea was observed in 0.15, 0.4, and 1 ppm males and in 0.4 and 1 ppm females. 2-YEAR STUDY IN RATS: Survival, Body Weights, Clinical Findings, and Urinalysis Groups of 60 male and 60 female rats were exposed to atmospheres containing 0, 0.01, 0.05, or 0.2 ppm (equivalent to 0, 0.11, 0.56, and 2.28 mg/m(3)) hexachlorocyclopentadiene. Survival rates and mean body weights of exposed rats were similar to those of the controls. No chemical-related clinical findings were observed in male or female rats during the 2-year study. No differences in urinalysis parameters at the 15-month interim evaluation could be attributed to exposure to hexachlorocyclopentadiene. Pathology Findings: No increases in neoplasm incidences could be attributed to hexachlorocyclorocyclopentadiene. Toxicity was limited to the respiratory tract and included an increase in the incidence of pigmentation of the respiratory epithelium of the nose, trachea, and the bronchi and bronchioles of the lung in both males and females. Exposure to hexachlorocyclopentadiene also caused an increase in the incidence of squamous metaplasia of the laryngeal epithelium of exposed females; the incidences in 0.01 and 0.2 ppm females were significantly greater than that of the controls. The severity of squamous metaplasia was minimal in all exposed and control females. 2-YEAR STUDY IN MICE: Survival, Body Weights, Clinical Findings, and Urinalysis Groups of 60 male and 60 female mice were exposed to atmospheres containing 0, 0.01, 0.05, or 0.2 ppm (equivalent to 0, 0.11, 0.56, and 2.28 mg/m(3)) hexachlorocyclopentadiene. The 2-year survival rate of female mice in the 0.2 ppm group was marginally lower than that of the controls due to a higher incidence of ovarian inflammation in 0.2 ppm females. Mean body weights of 0.2 ppm males (weeks 62 to 103) and females (throughout the study) were lower than those of the controls. No clinical findings in male or female mice were attributed to chemical exposure during the 2-year study. There were no chemical-related differences in urinalysis parameters at the 15-month interim evaluation. Pathology Findings: The site of toxicity of hexachlorocyclopentadiene exposure in mice in the 2-year study was the respiratory tract. Chemical-related pigmentation of the respiratory epithelium of the nose, trachea, and lung and suppurative inflammation of the nose were observed. No increased neoplasm incidences in males or females could be attributed to hexachlorocyclopentadiene exposure. STOP-EXPOSURE EVALUATION: Survival, Body Weights, and Clinical Findings Groups of male mice were exposed to atmospheres containing 0.2 ppm hexachlorocyclopentadiene for 33 or 66 weeks or 0.5 ppm for 26 or 42 weeks followed by exposure to air until the end of the study. Fifty male mice from each stop-exposure group were evaluated at 2 years. Two-year survival rates of stop exposure groups were similar to that of the controls. Final mean body weights of stop-exposure groups were similar to that of the controls. No chemical related clinical findings were observed. Pathology Findings: Nonneoplastic respiratory tract lesions similar to those observed in the core study were observed in males in the stop-exposure groups. Chemical-related pigmentation and inflammation of the respiratory epithelium were persistent as indicated by their presence in many male mice after recovery periods of 62 to 78 weeks, and the incidence and severity of the lesions were related to exposure concentration and duration. GENETIC TOXICOLOGY: Hexachlorocyclopentadiene was not mutagenic in Salmonella typhimurium strains TA98, TA100, TA1535, and TA1537 when tested with and without S9. Hexachlorocyclopentadiene did induce sister chromatid exchanges and chromosomal aberrations in cultured Chinese hamster ovary cells, with and without S9. No induction of sex-linked recessive lethal mutations was observed in male Drosophila melanogaster treated with hexachlorocyclopentadiene by feeding or injection, and no increase in the frequency of micronucleated erythrocytes was seen in male or female B6C3F1 mice exposed to hexachlorocyclopentadiene by inhalation for 13 weeks. CONCLUSIONS: Under the conditions of these 2-year studies, there was no evidence of carcinogenic activity of hexachlorocyclopentadiene in male or female F344/N rats or B6C3F1 mice exposed to 0.01, 0.05, or 0.2 ppm. Exposure of rats to hexachlorocyclopentadiene produced pigmentation of the respiratory epithelium of the nose, trachea (males), and bronchi and bronchioles of the lung. Squamous metaplasia of the laryngeal epithelium occurred in female rats exposed to hexachlorocyclopentadiene. Suppurative inflammation of the nose as well as pigmentation of the respiratory mucosal epithelium occurred in mice exposed to hexachlorocyclopentadiene. Synonyms: Perchlorocyclopentadiene, hexachloro-1,3-cyclopentadiene, HEX, HCPD, HCCP, HCCPD Trade Name: C-56-Graphlox

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of 4,4'-Thiobis(6- t -butyl- m -cresol) (CAS No. 96-69-5) in F344/N Rats and B6C3F1 Mice (Feed Studies).

4,4'-Thiobis(6- t -butyl- m -cresol) (TBBC) is used in the rubber and plastics industries as an antioxidant. TBBC is also used as a stabilizer in polyethylene and polyolefin packaging materials for foodstuffs. Toxicology and carcinogenesis studies were conducted by administering TBBC (99% pure) in feed to groups of male and female F344/N rats and B6C3F1 mice for 15 days, 13 weeks, and 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium and cultured Chinese hamster ovary cells. 15-DAY STUDY IN RATS: Groups of 10 male and 10 female F344/N rats were fed diets containing 0, 1,000, 2,500, 5,000, 10,000 or 25,000 ppm TBBC for 15 days. Rats given to 1,000, 2,500, 5,000, or 10,000 ppm received approximate doses of 95, 235, 335, or 365 mg TBBC per kilogram body weight per day (males) or 85, 220, 325, or 270 mg/kg per day (females). Approximate doses for rats receiving 25,000 ppm could not be calculated due to early deaths. All 25,000 ppm rats and three male and four female 10,000 ppm rats died. Surviving rats in the 10,000 ppm groups had a significant weight loss and the final mean body weights of 5,000 and 10,000 ppm male and female rats were significantly lower than those of the controls. Male and female rats exposed to 5,000, 10,000, or 25,000 ppm TBBC consumed markedly less feed than the controls. Diarrhea occurred in 5,000, 10,000, and 25,000 ppm males and females. The principal lesions attributed to the administration of TBBC were renal papillary and tubule necroses which occurred in 10,000 ppm rats. Focal necrosis or erosions of the glandular stomach also occurred in some 10,000 ppm rats. Changes observed in the thymus and spleen were attributed to debilitation or stress; bone marrow depletion was attributed to nutrient deficiency accompanying weight loss. 15-DAY STUDY IN MICE: Groups of 10 male and 10 female B6C3F1, mice were fed diets containing 0, 1,000, 2,500, 5,000, 10,000, or 25,000 ppm TBBC for 15 days. Mice given 1,000, 2,500, or 5,000 ppm received approximate doses of 285, 585, or 475 mg TBBC per kilogram body weight per day (males) or 360, 950, or 1,030 mg/kg per day (females). Approximate doses for mice given 10,000 or 25,000 ppm could not be calculated due to early deaths. All 10,000 and 25,000 ppm mice died, as did eight males and eight females given 5,000 ppm. A significant weight loss occurred in surviving 5,000 ppm males and females and the final mean body weights of 2,500 ppm females and 5,000 ppm males and females were significantly lower than those of the controls. Feed consumption by mice given 5,000, 10,000, or 25,000 ppm was markedly reduced. Diarrhea occurred in all 25,000 ppm mice and in most male and female mice given 5,000 or 10,000 ppm. Renal tubule necrosis occurred in eight males and three females in the 5,000 ppm groups. Lymphocytic depletion of Iymphoid tissues in many 5,000 ppm males and females was attributed to debilitation and stress or to nutrient deficiency accompanying weight loss. 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female F344/N rats were fed diets containing 0, 250, 500, 1,000, 2,500, or 5,000 ppm TBBC for 13 weeks. These exposure levels delivered approximate doses of 15, 30, 60, 165, or 315 mg TBBC per kilogram body weight per day (males) or 15, 35, 70, 170, or 325 mg/kg per day (females). All rats survived to the end of the study. The final mean body weight of 5,000 ppm males was 40% lower than that of the controls; the final mean body weight of 5,000 ppm females was 27% lower than that of the controls. Feed consumption by male and female rats exposed to 5,000 ppm TBBC was markedly lower than that by the controls throughout the study. The absolute and relative liver weights of 5,000 ppm females were significantly greater than those of the controls. Serum alkaline phosphatase (ALP) levels were significantly higher in 2,500 and 5,000 ppm males and slightly higher in 5,000 ppm females. Serum alanine aminotransferase levels were significantly higher in 2,500 and 5,000 ppm males and females. Hematocrit and hemoglobin concentrations and mean erythroions and mean erythrocyte volume (MCV) values were significantly lower in 1,000, 2,500, and 5,000 ppm males than in controls; MCV values were also significantly lower in 5,000 ppm females. A dose-related significant increase in forelimb and hindlimb grip strength was observed in exposed male and female rats. Histopathologic findings in the liver of 2,500 and 5,000 ppm males and females included hypertrophy of Kupffer cells, bile duct hyperplasia, and individual cell necrosis of hepatocytes; centrilobular hepatocyte hypertrophy also occurred in males and females exposed to 5,000 ppm TBBC. Macrophages were increased in size and number in the mesenteric Iymph nodes of males and females exposed to 5,000 ppm, and to a lesser extent in 2,500 ppm male and female rats. Pigmentation and degeneration of the renal cortical tubule epithelial cells was also present in males and females in the 2,500 and 5,000 ppm groups; cortical tubule necrosis occurred in 5,000 ppm males and females. 13-WEEK STUDY IN MICE: Groups of up to 10 male and 10 female B6C3F1 mice were fed diets containing 0, 100, 250, 500, 1,000, or 2,500 ppm TBBC for 13 weeks. These exposure levels delivered approximate doses of 15, 30, 65, 145, or 345 mg TBBC per kilogram body weight per day (males) or 10, 35, 60, 165, or 340 mg/kg per day (females). All mice survived to the end of the study. The final mean body weights of 2,500 ppm males and of 500,1,000, or 2,500 ppm females were significantly lower than those of the controls. Feed consumption by 2,500 ppm males averaged 24&percnt; lower than that by controls through week 3 and was similar to that by controls for the remainder of the study. Feed consumption by females receiving 2,500 ppm averaged 27&percnt; less than that by the controls during most of the study. The absolute and relative liver weights of males and females exposed to 2,500 ppm TBBC were slightly but significantly greater than those of the controls. Males exposed to 500, 1,000, or 2,500 ppm and females exposed to 2,500 ppm had significantly increased absolute and relative spleen weights. No clinical findings in mice were considered chemical related. Hematocrit concentrations and erythrocyte counts of males receiving 1,000 or 2,500 ppm were significantly less than those of the controls; hemoglobin concentration in males receiving 2,500 ppm was significantly less and mean erythrocyte volume was significantly less in males receiving 2,500 ppm. Females in the 1,000 and 2,500 ppm groups had significantly decreased hematocrit concentrations and erythrocyte counts; 2,500 ppm females also had significantly decreased hemoglobin concentrations and mean erythrocyte volumes. Kupffer cell hypertrophy, bile duct hyperplasia, and an increase in size and number of macrophages in mesenteric Iymph nodes were present in 2,500 ppm male and female mice. 2-YEAR STUDY IN RATS: Doses selected for the 2-year study of TBBC were based on the lower body weights and liver and kidney toxicity observed at 5,000 ppm in the 13-week study. Groups of 115 male and 75 female F344/N rats were fed diets containing 0, 500, 1,000, or 2,500 ppm TBBC for 2 years. Based on average daily feed consumption, these exposure levels resulted in a daily ingestion of TBBC of approximately 20, 40, or 100 mg/kg body weight for males and 20, 45, or 120 mg/kg body weight for females. Hematology, clinical chemistry, and urinalysis evaluations were performed on 15 male and 15 female rats from each group at 3, 9, and 15 months. Also at 15 months, an additional 10 male and 10 female rats from each group were evaluated for histopathology, hematology, and clinical chemistry. Forty male rats per group were evaluated for neurotoxic effects. Survival, Body Weights, Feed Consumption, and Clinical Findings: Two-year survival rates and mean body weights of exposed male and female rats were generally similar to those of the controls. The mean body weights of 2,500 ppm male rats were slightly lower than those of the controls throughout the study. At week 65, the mean body weight of 2,500 ppm females was 14&percnt; lower than that of the controls, but the final mean body weight of this group was 6&percnt; lower than that of the control group. Feed consumption, behavior, and general health and appearance of exposed male and female rats were similar to those of the controls. Hematology and Clinical Chemistry: Results of the hematology evaluation were not uniformly consistent at 3, 9, and 15 months in one set of rats, nor were they consistent between the two sets of rats evaluated at 15 months. Slight but significant decreases in hematocrit levels, hemoglobin concentrations, and erythrocyte counts were observed in the 1,000 and 2,500 ppm groups in one set of males at 15 months. Similar significant decreases in hematocrit level and hemoglobin concentration occurred in 2,500 ppm females at 9 months. Mean erythrocyte hemoglobin and mean erythrocyte hemoglobin concentration of 2,500 ppm females were also significantly lower than those of controls at 9 months and in both sets of female rats evaluated at 15 months. Platelet counts of 2,500 ppm male and female rats were slightly but significantly higher than those of controls at 3 and 9 months. Platelet counts were also slightly but significantly increased in 2,500 ppm males of one set evaluated at 15 months, and in 2,500 ppm females of the second set evaluated at 15 months. Serum activities of alkaline phosphatase, alanine aminotransferase, and sorbitol dehydrogenase in 2,500 ppm males were significantly greater than those in the controls at 3, 9, and 15 months. Alkaline phosphatase activities in both sets of 1,000 ppm males evaluated at 15 months were also significantly greater than those of controls. Serum activities of alanine aminotransferase and sorbitol dehydrogenase in 2,500 ppm females were also significantly greater than those in controls at 3, 9, and 15 months. Neurotoxicity Findings: There were no significant inhibitory effects of TBBC on motor nerve excitability or conduction, neuromuscular transmission, or muscle contractility. There were no microscopic lesions in the sciatic nerve, quadriceps muscle, or teased nerve preparations of sciatic nerve that could be attributed to TBBC administration. Pathology Findings: At the 15-month interim evaluation, the absolute and relative liver weights of 2,500 ppm female rats were significantly greater than those of controls; at 15 months and at the end of the study, the incidences of Kupffer cell hypertrophy, hepatocyte cytoplasmic vacuolization, and mixed cell foci were also significantly increased. At the end of the study, the incidence of hepatocellular fatty change was significantly increased in 2,500 ppm females. The incidence of Kupffer cell hypertrophy was significantly increased in 2,500 ppm males at 15 months and at 2 years; the incidence of cytoplasmic vacuolization was significantly increased in all exposed males at 15 months but only moderately increased in 1,000 and 2,500 ppm males at 2 years; the incidence of basophilic foci was significantly increased in 2,500 ppm males at 15 months and the incidence of mixed cell foci was significantly increased in 1,000 and 2,500 ppm male rats at 2 years. The incidences of hepatocellular adenoma or carcinoma (combined) in exposed male rats were not significantly greater than that in the controls (0 ppm, 1/50; 500 ppm, 3/50; 1,000 ppm, 3/50; 2,500 ppm, 5/49), were within the historical control range, and were not considered chemical related. The severity of nephropathy was significantly increased in 2,500 ppm female rats. There was a significant negative trend in the incidence of mammary gland fibroadenoma, adenoma, or carcinoma (combined) in female rats (32/50, 24/50, 11/50, 16/50), and the incidences of fibroadenoma in 1,000 and 2,500 ppm females were significantly less than that of the controls. 2-YEAR STUDY IN MICE: Because of the reduction in body weights, the increase in liver and spleen weights, and the accompanying histopathologic changes in the liver of 2,500 ppm male and female mice in the 13-week study, the doses selected for the 2-year study were 250, 500, and 1,000 ppm. Groups of 80 male and 80 female mice were fed diets containing 0, 250, 500, or 1,000 ppm TBBC for 2 years. Based on average daily feed consumption, these exposure levels resulted in the daily ingestion of approximately 30, 60, or 145 mg TBBC/kg body weight for males and 45, 110, or 255 mg TBBC/kg body weight for females. Nine or 10 animals from each exposure group were evaluated at 3, 9, and 15 months. Survival, Body Weights, Feed Consumption, and Clinical Findings: Two-year survival rates of exposed male and female mice were similar to those of the controls. The final mean body weights of male and female mice exposed to 1,000 ppm were 8&percnt; and 18&percnt; lower than those of the controls, respectively. The final mean body weights of females exposed to 250 or 500 ppm were 8&percnt; to 9&percnt; lower than that of the controls. Feed consumption by exposed males was similar to that by controls, and there were no clinical findings attributed to TBBC administration. Hematology and Clinical Chemistry: Hematocrit level, hemoglobin concentration, and erythrocyte count in 1,000 ppm male mice were significantly lower than those in controls at the 15-month interim evaluation. Serum alkaline phosphatase activities in 1,000 ppm males were slightly but significantly greater than those in controls at 3 and 9 months, as was the serum alkaline phosphatase activity in 1,000 ppm females at 9 months. Serum levels of total bilirubin in all exposed groups of males were significantly greater than those in controls at 9 and 15 months. Pathology Findings: In the liver of male mice, negative trends in the incidences of fatty change, clear cell foci, and adenoma or carcinoma combined occurred at the end of the 2-year study. There were no compound-related increased incidences of neoplasms or nonneoplastic lesions in mice receiving TBBC for 2 years. A negative trend in the incidence of fatty change in the liver of male mice also occurred at 15 months. GENETIC TOXICOLOGY: 4,4'-Thiobis(6- t -butyl- m -cresol) was not mutagenic in Salmonella typhimurium strains TA98, TA100, TA1535, or TA1537 with or without exogenous metabolic activation (S9). Sister chromatid exchanges were induced in cultured Chinese hamster ovary cells treated with TBBC, with and without S9, but no increases in chromosomal aberrations were noted in cultured Chinese hamster ovary cells after treatment with TBBC. CONCLUSIONS: Under the conditions of these 2-year feed studies, there was no evidence of carcinogenic activity of 4,4'-thiobis(6- t -butyl- m -cresol) in male or female F344/N rats administered 500, 1,000, or 2,500 ppm or in male or female B6C3F1, mice administered 250, 500, or 1,000 ppm. Nonneoplastic lesions associated with exposure to TBBC included: Kupffer cell hypertrophy, cytoplasmic vacuolization, and mixed cell foci in the liver of male and female rats, fatty change in the liver of female, rats, and an increase in the severity of nephropathy in the kidney of female rats. In addition, decreased incidences of fibroadenoma, adenoma, or carcinoma (combined) were observed in the mammary gland of female rats. Decreases also occurred in the incidences of fatty change, clear cell foci, and adenoma or carcinoma (combined) in the liver of male mice. Synonyms: 4,4'-Thiobis(6- t -butyl-3-cresol); bis(3- t -butyl-4-hydroxy-6-methylphenyl)sulfide

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of o-Benzyl-p-Chlorophenol (CAS No. 120-32-1) in F344/N Rats and B6C3F1 Mice (Gavage Studies).

o-Benzyl-p-chlorophenol is an aryl halide biocide with widespread use in hospitals and households as a broad-spectrum germicide in disinfectant solutions and soap formulations for general cleaning and disinfecting. Human exposure to o-benzyl-p-chlorophenol occurs by absorption through the skin and mucous membranes and by ingestion. Toxicity and carcinogenicity studies were conducted by administering o-benzyl-p-chlorophenol (approximately 97% pure) in corn oil by gavage to male and female F344/N rats and B6C3F1 mice for 16-days, 13-weeks, and 2-years. Clinical pathology parameters were evaluated during the 2-year rat study. Genetic toxicity studies were conducted in Salmonella typhimurium, cultured Chinese hamster ovary cells, L5178Y mouse lymphoma cells, and cultured human lymphoblast cells. 16-DAY STUDY IN RATS: Groups of five male and five female rats were administered o-benzyl-p-chlorophenol in corn oil by gavage at doses of 0, 62.5, 125, 250, 500, or 1,000 mg/kg body weight 5 days a week over a 16-day period. Two 1,000 mg/kg female rats died and these deaths were attributed to chemical administration. The mean body weight gains of 1,000 mg/kg males and females were significantly lower than those of the controls. Clinical findings in 1,000 mg/kg males and females included diarrhea and rough hair coat. Absolute and relative kidney and liver weights of 250, 500, and 1,000 mg/kg males and 1,000 mg/kg females were significantly greater than those of the controls. Absolute and relative thymus weights of 500 and 1,000 mg/kg males and 250, 500, and 1,000 mg/kg females were significantly lower than those of the controls. At necropsy, dilatation of the cecum was observed in male and female rats; the incidence generally increased with dose. The dilated cecum of some dosed rats had necrosis of the mucosal epithelium. Mild to moderate nephropathy was observed in all 1,000 mg/kg male and female rats. Minimal nephropathy occurred in one rat receiving 62.5 mg/kg, two rats each from the 125 and 250 mg/kg groups, and seven rats in the 500 mg/kg groups. The incidence and severity of nephropathy increased with dose. 16-DAY STUDY IN MICE: Groups of five male and five female mice were administered o-benzyl-p-chlorophenol in corn oil by gavage at doses of 0, 62.5, 125, 250, 500, or 1,000 mg/kg body weight 5 days a week over a 16-day period. Deaths occurred only in the 1,000 mg/kg groups, in which three males and all females died. Mean body weight gains of dosed male and female mice were generally similar to those of the controls. Clinical findings in male and female high-dose mice included rough hair coat and postural changes. Absolute and relative liver weights of 500 and 1,000 mg/kg males and 500 mg/kg females (the highest dose group of females surviving) were significantly greater than those of the controls. Necropsy findings included dilatation of the cecum. Nephropathy occurred in 500 and 1,000 mg/kg mice (500 mg/kg, 2/10; 1,000 mg/kg, 6/10). 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female rats were administered o-benzyl-p-chlorophenol in corn oil by gavage at doses of 0, 30, 60, 120, 240, or 480 mg/kg body weight 5 days a week for 13 weeks. No deaths were attributed to o-benzyl-p-chlorophenol administration; however, the deaths of five male rats were attributed to gavage trauma. Mean body weight gains of all dosed rats were generally similar to those of the controls. Clinical findings included yellow-red staining of the urogenital region hair coat of all dosed females. The albumin/globulin ratios in 120, 240, and 480 mg/kg male rats increased with dose and were the result of net decreases in total globulin. Administration of o-benzyl-p-chlorophenol caused no significant alterations in hematologic or urinalysis parameters. Absolute and relative kidney weights were significantly greater and the absolute and relative thymus weights were significantly lower in 480 mg/kg male and female rats and in 240 mg/kg female rats. No gross lesions related to compound administration were observed at necropsy. Nephropathy of mild to moderate derate severity occurred in 480 mg/kg male and female rats and in 240 mg/kg male rats. Few or no lesions occurred in other dosed rats and none occurred in controls. 13-WEEK STUDIES IN MICE: In the first 13-week study, groups of 10 male and 10 female mice were administered o-benzyl-p-chlorophenol in corn oil by gavage at doses of 0, 30, 60, 120, 240, or 480 mg/kg body weight 5 days a week for 13 weeks. Survival, mean body weight gains, and clinical findings of dosed animals were similar to those of the controls throughout the study. The Pathology Working Group confirmed that no microscopic lesions were observed that could definitively be associated with o-benzyl-p-chlorophenol administration. On the basis of these findings, a second 13-week study was performed using higher doses. In the second 13-week study, groups of 15 male and 15 female mice were administered o-benzyl-p-chlorophenol in corn oil by gavage at doses of 0, 500, 650, 800, or 1,000 mg/kg body weight 5 days a week for up to 13 weeks. Five male and five female mice from each group were evaluated after 2 weeks, with the remainder (up to 10 per sex) evaluated at the end of the study. One 500 mg/kg mouse, three 650 mg/kg mice, 14 mice receiving 800 mg/kg, and 19 mice administered 1,000 mg/kg died before the end of the study. Mean body weight gains of dosed male and female mice that received 500 or 800 mg/kg were lower than those of the controls. Absolute and relative liver weights of 800 mg/kg males and all surviving dosed females were significantly greater than those of the controls. Absolute and relative kidney weights of 500, 650, and 800 mg/kg male mice were slightly lower than those of the controls, and those of female mice were similar to those of the controls. The incidence and severity of nephropathy increased with time and with increasing dose of o-benzyl-p-chlorophenol. Significant nephropathy was present at all doses, with mild nephropathy present at the 500 mg/kg dose. Acute necrotizing, suppurative inflammation of the olfactory epithelium was noted in all dose groups, with severity increasing with dose. These lesions were considered to be directly related to the caustic nature of o-benzyl-p-chlorophenol following retrograde exposure after gavage, with the presence of foreign material likely due to retrograde migration of the chemical. 2-YEAR STUDY IN RATS: Groups of 80 male and 80 female rats were administered o-benzyl-p-chlorophenol in corn oil by gavage 5 days a week for 103 weeks. The doses were 0, 30, 60, or 120 mg/kg body weight for male rats and 0, 60, 120, or 240 mg/kg body weight for female rats. After 3 and 15 months, 7 to 10 male and 8 to 10 female rats were evaluated for organ weights and clinical pathology, and control and high-dose rats were evaluated for histopathology. Survival, Body Weights, and Clinical Findings: Survival of dosed male and female rats was similar to that of the controls. Mean body weights of dosed rats were generally similar to those of the controls. No chemical-related clinical findings were observed except yellow staining of the urogenital area hair coat in dosed female rats; staining was observed earlier in high-dose female rats. Pathology Findings: Severe, time- and dose-related nephropathy was observed in male and female rats, occurring as early as 3 months after the beginning of chemical administration (females). In male rats dosed for as long as 2 years, secondary hyperparathyroidism developed, with parathyroid gland hyperplasia, mineralization of the kidney and glandular stomach, and fibrous osteodystrophy occurring in the high-dose group. The severity of these lesions was greater in males. The kidney was the only organ in which chemical related increased incidences of neoplasms may have occurred. One renal tubule adenoma occurred in a control male rat, one renal tubule adenoma and one transitional cell carcinoma occurred in high-dose female rats, and one transitional cell carcinoma occurred in a mid-dose female. One renal tubule carcinoma was observed in a high-dose male rat. 2-YEAR STUDY IN MICE: Groups of 70 male and 70 female mice were administered o-benzyl-p-chlorophenol in corn oil by gavage at doses of 0, 120, 240, or 480 mg/kg body weight 5 days a week for 103 weeks. Ten male and 9 or 10 female mice were evaluated after 3 and 15 months for organ weights and histopathology; the remaining 50 male and 50 female mice were evaluated at the end of the study. Survival, Body Weights, and Clinical Findings: Survival of high-dose male and female mice was lower than that of the controls, which was associated in part with dose-related increases in the incidence and severity of nephropathy. The final mean body weights of all dosed males and mid- and high-dose females were lower than those of the controls. Chemical-related clinical findings included emaciation, abnormal posture, rough hair coat, and hypoactivity. Pathology Findings: Nephropathy occurred in most dosed males and females, and the incidence and severity increased with time and dose. Fibrous osteodystrophy of bone, mineralization of the glandular stomach, and squamous hyperplasia of the forestomach occurred in male and female mice. In the standard evaluation, the combined incidence of renal tubule adenoma and carcinoma was increased in 240 mg/kg male mice. Six renal tubule adenomas and three renal tubule carcinomas occurred in dosed male mice. No renal neoplasms occurred in female mice. Due to the marginal increase in renal neoplasia, and the small size of renal neoplasms, an extended evaluation of the kidney was conducted. No significant alteration in the neoplasm incidences were observed in female mice. However, a dose-related increased trend of renal tubule adenoma was observed in male mice. Combination of the extended evaluation with the original evaluation resulted in an increased incidence of renal tubule adenomas in the 480 mg/kg males and an increased incidence of renal tubule adenomas or carcinomas in both the 240 and 480 mg/kg males. GENETIC TOXICOLOGY: o-Benzyl-p-chlorophenol did not induce gene mutations in Salmonella typhimurium strains TA98, TA100, TA1535, or TA1537 and did not induce sister chromatid exchanges or chromosomal aberrations in cultured Chinese hamster ovary cells. These tests were performed with and without exogenous metabolic activation (S9). Positive results were obtained, however, in gene mutation tests conducted with LS178Y mouse Lymphoma cells and TK6 human lymphoblast cells in the absence of S9. CONCLUSIONS: Under the conditions of these 2-year gavage studies, there was no evidence of carcinogenic activity of o-benzyl-p-chlorophenol in male F344/N rats receiving 30, 60, or 120 mg/kg body weight. There was equivocal evidence of carcinogenic activity of o-benzyl-p-chlorophenol in female F344/N rats based on the occurrence of two rare renal transitional cell carcinomas. There was some evidence of carcinogenic activity of o-benzyl-p-chlorophenol in male B6C3F1 mice based on increased incidences of renal tubule adenoma and renal tubule adenoma or carcinoma (combined). There was no evidence of carcinogenic activity of o-benzyl-p-chlorophenol in female B6C3F1, mice receiving 120, 240, or 480 mg/kg. o-Benzyl-p-chlorophenol was nephrotoxic for male and female F344/N rats and B6C3F1 mice. The severity of nephropathy was increased in male and female rats and the incidence and severity of nephropathy was increased in male and female mice. The incidence and severity of nephropathy increased with length of treatment. Other lesions considered to be associated with the nephropathy and the secondary hyperparathyroidism in male rats and in male and female mice included fibrous osteodystrophy and soft tissue mineralization. Increased incidences of squamous cell hyperplasia of the forestomach were observed in mice. Synonyms: 2-benzyl-4-chlorophenol, 4-chloro-2-benzylphenol, 4-chloro-2-(phenylmethyl)phenol, 4-chloro-alpha-phenol o-cresol, p-chloro-o-benzylphenol, 2-hydroxy-5-chlorodiphenylmethane Trade names: Bio-Clave, Chlorophene, Clorofene, Clorophene, Ketolin H, Nipacide BCPR, Preventol BPR, Santophen 1, Septiphene

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of Tricresyl Phosphate (CAS No. 1330-78-5) in F344/N Rats and B6C3F1 Mice (Gavage and Feed Studies).

Tricresyl phosphate is an organophosphate plasticizer widely used in vinyl plastics and as a fire retardant additive for hydraulic fluids. Toxicology and carcinogenesis studies were conducted by administering a mixed isomer preparation of 79% tricresyl phosphate esters (consisting of 21% tri- m-cresyl phosphate, 4% tri- p-cresyl phosphate, less than 1% tri- o-cresyl phosphate, and other unidentified tricresyl phosphate esters) by gavage to groups of F344/N rats and B6C3F1 mice for 16 days and 13 weeks, and in feed to groups of F344/N rats and B6C3F1 mice for 13 weeks and 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium and cultured Chinese hamster ovary cells. 16-DAY GAVAGE STUDY IN RATS: Groups of 10 male and 10 female rats received tricresyl phosphate in corn oil by gavage at doses of 0, 360, 730, 1,450, 2,900, or 5,800 mg/kg body weight, 5 days per week, for a total of 13 or 14 doses in a 16-day period. One female receiving 1,450 mg/kg and five males and eight females receiving 2,900 mg/kg died before the end of the study. Final mean body weights of male and female rats that received 1,450, 2,900, or 5,800 mg/kg were significantly lower than those of the controls. Necrosis of the mandibular lymph node, spleen, and thymus occurred primarily in rats receiving 2,900 and 5,800 mg/kg. Diffuse aspermatogenesis occurred in the testes of male rats that received 2,900 and 5,800 mg/kg. Changes in neurobehavioral parameters in groups that received 1,450, 2,900, or 5,800 mg/kg were confounded by mortality and reduced body weights and were not attributed to a direct neurotoxic response. 16-DAY GAVAGE STUDY IN MICE: Groups of 10 male and 10 female mice received tricresyl phosphate in corn oil by gavage at doses of 0, 360, 730, 1,450, 2,900, or 5,800 mg/kg body weight, 5 days per week, for a total of 13 or 14 doses in a 16-day period. Five males and all females that received 1,450 mg/kg, all mice that received 2,900 mg/kg, and four males and one female that received 5,800 mg/kg died before the end of the study. Final mean body weights of male mice that received 1,450 and 5,800 mg/kg were significantly lower than that of the controls. Final mean body weights of female mice that received 360, 730, or 5,800 mg/kg were significantly greater than that of the controls. Necrosis of the mandibular lymph node, thymus, and spleen occurred primarily in mice receiving 2,900 and 5,800 mg/kg. Hindlimb grip strengths of male mice that received 360 and 1,450 mg/kg and male and female mice that received 730 and 5,800 mg/kg were significantly lower than those of the controls at the end of the study. 13-WEEK GAVAGE STUDY IN RATS: Groups of 10 male and 10 female rats received tricresyl phosphate in corn oil by gavage at doses of 0, 50, 100, 200, 400, or 800 mg/kg body weight. All rats survived to the end of the study. Final mean body weights of male rats receiving 200, 400, and 800 mg/kg were significantly lower than that of the controls. Cytoplasmic vacuolization of the adrenal cortex occurred in all dosed groups and the severity increased with dose. Ovarian interstitial cell hypertrophy occurred in all dosed groups of females. Atrophy of the seminiferous tubules occurred in male rats that received 400 and 800 mg/kg. There were no biologically significant changes in neurobehavioral parameters in rats. 13-WEEK GAVAGE STUDY IN MICE: Groups of 10 male and 10 female mice received tricresyl phosphate in corn oil by gavage at doses of 0, 50, 100, 200, 400, or 800 mg/kg body weight. All mice survived to the end of the study. Final mean body weights of male mice receiving 200 mg/kg and of male and female mice receiving 400 and 800 mg/kg were significantly lower than those of the controls. Cytoplasmic vacuolization of the adrenal cortex occurred in all dosed groups of mice and the severity increased with dose. Ovarian interstitial cell hypertrophy was present in all dosed groups of female mice. Multifocal degeneration of the spinal cord occurred in males and females that received 100, 200, 400, and 800 mg/kg, and multifocal degenerg/kg, and multifocal degeneration of the sciatic nerve occurred in males that received 200, 400, and 800 mg/kg and females that received 100, 200, 400, and 800 mg/kg. Hindlimb grip strengths of male mice that received 200, 400, or 800 mg/kg were significantly lower than that of the controls at the end of the study. 13-WEEK FEED STUDY IN RATS: Groups of 10 male and 10 female rats were fed diets containing 0, 900, 1,700, 3,300, 6,600, or 13,000 ppm of tricresyl phosphate. All rats survived to the end of the study. Final mean body weights of males and females exposed to 6,600 and 13,000 ppm and females exposed to 3,300 ppm were significantly lower than those of controls. Feed consumption by male and female rats exposed to 13,000 ppm was lower than that by controls during the first week of the study. Dietary levels of 900, 1,700, 3,300, 6,600 or 13,000 ppm tricresyl phosphate were estimated to deliver daily doses of 55, 120, 220, 430, or 750 mg/kg body weight (males) and 65, 120, 230, 430, or 770 mg/kg (females). There were no biologically significant changes in neurobehavioral parameters in rats. Cytoplasmic vacuolization of the adrenal cortex occurred in all exposed groups of rats. Hyperplasia of ovarian interstitial cells and inflammation of the ovarian interstitium occurred in all exposed groups of females. Renal papillary edema and renal papillary necrosis occurred in 13,000 ppm males and females and in 6,600 ppm females. Basophilic hypertrophy of the pituitary gland pars distalis and atrophy of the seminiferous tubules occurred in 6,600 and 13,000 ppm males. Dose selection for the 2-year study in rats was based on lower mean body weights; toxic responses observed in the kidney, pituitary gland, and testis of males and the kidney of females exposed to 6,600 and 13,000 ppm; the presence of cytoplasmic vacuolization of the adrenal cortex in exposed males and females; and the occurrence of ovarian interstitial cell hyperplasia in females exposed to 900 and 1,700 ppm. 13-WEEK FEED STUDY IN MICE: Groups of 10 male and 10 female mice were fed diets containing 0, 250, 500, 1,000, 2,100, or 4,200 ppm of tricresyl phosphate. All mice survived to the end of the study. Mean body weights of 4,200 ppm males and of females exposed to 2,100 and 4,200 ppm were lower than those of controls throughout the study. Feed consumption by females exposed to 1,000, 2,100, or 4,200 ppm was lower than that by controls during week 12. Dietary levels of 250, 500, 1,000, 2,100, or 4,200 ppm tricresyl phosphate were estimated to deliver average daily doses of 45, 110, 180, 380, or 900 mg/kg body weight (males) and 65, 130, 230, 530, or 1,050 mg/kg (females). Interpretation of grip strength changes observed in groups receiving 2,100 or 4,200 ppm were confounded by the reduced body weights of these groups. Cytoplasmic vacuolization of the adrenal cortex occurred in all exposed groups of male and female mice with the exception of 250 ppm males. Papillary hyperplasia of the gallbladder mucosa occurred in male mice exposed to 500 ppm or more and in female mice exposed to 1,000 ppm or more. Axonal degeneration occurred in males and females exposed to 2,100 and 4,200 ppm and females exposed to 1,000 ppm. Renal tubule regeneration occurred in all 4,200 ppm male mice. Dose selection for the 2-year study in mice was based on the presence of axonal degeneration at concentrations of 1,000 ppm or more and cytoplasmic vacuolization of the adrenal cortex at concentrations of 500 ppm or more in males and in all exposed groups of females. 2-YEAR FEED STUDY IN RATS: Groups of 95 male and 95 female rats were fed diets containing 0, 75, 150, or 300 ppm of tricresyl phosphate. An additional group of 95 male and 95 female rats were fed diets containing 600 ppm of tricresyl phosphate for 22 weeks and then received only control feed. After 3, 9, and 15 months of chemical exposure, up to 15 males and 15 females per group were evaluated for forelimb and hindlimb grip strength, then necropsied and evaluated for histopathologic lesions. Survival, Mean Body Weights, and Feed Consumption: Survival of exposed rats was similar to that of controls. The final mean body weights of all exposed groups of males and females were similar to those of the controls. Feed consumption by exposed groups of male and female rats was similar to that by the controls. Dietary levels of 75, 150, or 300 ppm tricresyl phosphate were estimated to deliver average daily doses of 3, 6, or 13 mg/kg body weight (males) and 4, 7, or 15 mg/kg (females). Pathology Findings: There were no chemical-related increased incidences of neoplasms in rats. Cytoplasmic vacuolization of the adrenal cortex occurred in 600 ppm males and 150, 300, and 600 ppm females at the 3-month interim evaluation. At 9 and 15 months, cytoplasmic vacuolization occurred only in female rats, primarily in the 300 ppm group. Cytoplasmic vacuolization of the adrenal cortex and ovarian interstitial cell hyperplasia occurred in female rats exposed to 300 ppm throughout the 2-year study and the incidence and severity were significantly increased at the end of the study. 2-YEAR FEED STUDY IN MICE: Groups of 95 male and 95 female mice were fed diets containing 0, 60, 125, or 250 ppm of tricresyl phosphate. After 3, 9, and 15 months of chemical exposure, up to 15 males and 15 females per group were evaluated for forelimb and hindlimb grip strength, then necropsied and evaluated for histopathologic lesions. Survival, Mean Body Weights, and Feed Consumption: Survival of exposed groups of male and female mice was similar to that of the controls. The final mean body weights of males and females receiving tricresyl phosphate were similar to those of controls. Feed consumption by exposed groups of male and female mice was similar to that by the controls. Dietary levels of 60, 125, or 250 ppm tricresyl phosphate were estimated to deliver average daily doses of 7, 13, or 27 mg/kg body weight (males) and 8, 18, or 37 mg/kg (females). Pathology Findings: There were no chemical-related increased incidences of neoplasms in mice. Ceroid pigmentation of the adrenal cortex occurred in all groups of mice throughout most of the 2-year study, with the exception of 60 and 125 ppm females at the 3-month interim evaluation; however, the severity was markedly increased in female mice receiving 250 ppm. Incidences of clear cell foci, fatty change, and ceroid pigmentation of the liver were significantly increased in male mice that received 125 or 250 ppm. GENETIC TOXICOLOGY: Tricresyl phosphate was not mutagenic in Salmonella typhimurium strains TA98, TA100, TA1535, or TA1537, nor did it induce chromosomal aberrations or sister chromatid exchanges in cultured Chinese hamster ovary cells. These in vitro assays were all conducted with and without exogenous metabolic activation (S9). CONCLUSIONS: Under the conditions of these 2-year feed studies, there was no evidence of carcinogenic activity of tricresyl phosphate in male or female F344/N rats that received 75, 150, or 300 ppm. There was no evidence of carcinogenic activity of tricresyl phosphate in male or female B6C3F1 mice that received 60, 125, or 250 ppm. Nonneoplastic lesions associated with exposure to tricresyl phosphate included cytoplasmic vacuolization of the adrenal cortex and ovarian interstitial cell hyperplasia in female rats, increased incidences of clear cell focus, fatty change, and ceroid pigmentation of the liver in male mice, and increased severity of ceroid pigmentation of the adrenal cortex in female mice.

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of Barium Chloride Dihydrate (CAS No. 10326-27-9) in F344/N Rats and B6C3F1 Mice (Drinking Water Studies).

Barium chloride dihydrate, a white crystalline granule or powder, is used in pigments, aluminum refining, leather tanning and coloring, the manufacture of magnesium metal, ceramics, glass, and paper products, as a pesticide, and in medicine as a cardiac stimulant. Toxicology and carcinogenicity studies were conducted by administering barium chloride dihydrate (99% pure) in drinking water to F344/N rats and B6C3F1 mice for 15 days, 13 weeks, and 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium, cultured Chinese hamster ovary cells, and mouse lymphoma cells. 15-DAY STUDY IN RATS: Groups of five males and five females received barium chloride dihydrate in the drinking water at concentrations of 0, 125, 250, 500, 1,000, or 2,000 ppm for 15 days, corresponding to average daily doses of 10, 15, 35, 60, or 110 mg barium/kg body weight to males and females. No chemical-related deaths, differences in final mean body weights, or clinical findings of toxicity were observed. Water consumption by male and female rats exposed to 2,000 ppm was slightly less (S16%) than controls during week 2. There were no significant differences in absolute or relative organ weights between exposed and control rats. No biologically significant differences in hematology, clinical chemistry, or neurobehavioral parameters occurred in rats. 15-DAY STUDY IN MICE: Groups of five males and five females received barium chloride dihydrate in the drinking water at concentrations of 0, 40, 80,173, 346, or 692 ppm for 15 days, corresponding to average daily doses of 5,10, 20, 40, or 70 mg barium/kg body weight to males and 5, 10, 15, 40, or 85 mg barium/kg body weight to females. No chemical-related deaths, differences in mean body weights or in water consumption, or clinical findings of toxicity were observed in mice. The relative liver weight of males receiving 692 ppm was significantly greater than that of the controls. The absolute and relative liver weights of females that received 692 ppm were significantly greater than those of the controls. No histopathologic evidence of toxicity was observed in mice. 13-WEEK STUDY IN RATS: Groups of 10 males and 10 females received barium chloride dihydrate in the drinking water at concentrations of 0, 125, 500, 1,000, 2,000, or 4,000 ppm for 13 weeks, corresponding to average daily doses of 10, 30, 65, 110, or 200 mg barium/kg body weight to males and 10, 35, 65, 115, or 180 mg barium/kg body weight to females. Three males and one female in the 4,000 ppm groups died during the last week of the study. The final mean body weights of male and female rats receiving 4,000 ppm were significantly lower (13% and 8%) than those of the controls. Water consumption by male and female rats in the 4,000 ppm groups was approximately 30% lower than that by the controls. No clearly chemical-related clinical findings of toxicity or neurobehavioral or cardiovascular effects were noted. Serum phosphorus levels in 2,000 and 4,000 ppm male and female rats were significantly higher than those in controls, but there were no biologically significant differences in hematology parameters or in serum sodium, potassium, or calcium levels. Renal tubule dilatation in the outer stripe of the outer medulla and cortex occurred in male and female rats receiving 4,000 ppm. 13-WEEK STUDY IN MICE: Groups of 10 males and 10 females received barium chloride dihydrate in the drinking water at concentrations of 0, 125, 500, 1,000, 2,000, or 4,000 ppm for 13 weeks, corresponding to average daily doses of 15, 55, 100, 205, or 450 mg barium/kg body weight to males and 15, 60, 110, 200, or 495 mg barium/kg body weight to females. Six males and seven females that received 4,000 ppm and one male that received 125 ppm died during the study. Final mean body weights of male and female mice receiving 4,000 ppm were significantly lower (>30%) than those of controls. Water consumption by male mice in the 4,000 ppm group was 18% lower than that by the controls; water consumption by other exposed groups of male and female mice was similar to thatd groups of male and female mice was similar to that by the controls. Clinical findings of toxicity were limited to debilitation in the surviving male and female mice receiving 4,000 ppm. The absolute and/or relative liver weights of mice receiving 1,000, 2,000, and 4,000 ppm were significantly lower than those of the controls. Multifocal to diffuse nephropathy characterized by tubule dilatation, regeneration, and atrophy occurred in 4,000 ppm male and female mice. 2-YEAR STUDY IN RATS: Groups of 60 males and 60 females received barium chloride dihydrate in the drinking water at concentrations of 0, 500, 1,250, or 2,500 ppm for 104 (males) or 105 weeks (females), corresponding to average daily doses of 15, 30, or 60 mg barium/kg body weight for males and 15, 45, or 75 mg barium/kg body weight for females. The high dose of 2,500 ppm was selected based on decreased final mean body weights, mortality, decreased water consumption, and chemical-related kidney lesions observed in the 4,000 ppm groups in the 13-week study. Survival, Body Weights, Water Consumption, and Clinical Findings: Two-year survival of exposed male and female rats was similar to that of the controls. The final mean body weights of male and female rats that received 2,500 ppm were (5&percnt; and 11&percnt;) lower than those of controls. Beginning as early as week 5, water consumption by male and female rats receiving 2,500 ppm was substantially lower than that by controls (male: 11&percnt; to 30&percnt;; female: 19&percnt; to 33&percnt;). There were no chemical-related clinical findings. Hematology and Clinical Chemistry: There were no chemical-related differences in hematology or clinical chemistry parameters in male or female rats. Special Studies: At the 15-month interim evaluation, the plasma barium concentrations (mg/ml) were significantly increased in males receiving 1,250 and 2,500 ppm and in all exposed groups of females (male: 0 ppm, 0.98; 500 ppm, 1.00; 1,250 ppm, 1.23; 2,500 ppm, 1.68; female: 0 ppm, 0.74; 500 ppm, 0.99; 1,250 ppm, 0.97; 2,500 ppm, 1.43). Barium levels in bone in rats from the 2,500 ppm groups were about 400 times greater than those in the controls. Pathology Findings: At the end of 2 years, there were no increased incidences of neoplasms or nonneoplastic lesions that could be attributed to barium chloride dihydrate. However, there were dose-related decreased incidences of adrenal medulla pheochromocytomas and mononuclear cell leukemia in male rats. 2-YEAR STUDY IN MICE: Groups of 60 males and 60 females received barium chloride dihydrate in the drinking water at concentrations of 0, 500, 1,250, or 2,500 ppm for 103 (males) or 104 weeks (females), corresponding to average daily doses of 30, 75, or 160 mg barium/kg body weight for males and 40, 90, or 200 mg barium/kg body weight for females. The high dose of 2,500 ppm was selected based on decreased final mean body weights, mortality, decreased water consumption, and chemical-related kidney lesions observed in the 4,000 ppm groups in the 13-week study. Survival, Body Weights, Water Consumption, and Clinical Findings: Two-year survival of male and female mice receiving 2,500 ppm was significantly lower than that of the controls due to renal toxicity. Final mean body weights of 2,500 ppm males and females were 9% and 12% lower than those of controls. Water consumption by male and female mice receiving barium chloride was similar to that by the controls. There were no chemical-related clinical findings. Hematology and Clinical Chemistry: There were no differences in hematology or clinical chemistry parameters measured at the 15-month interim evaluation. Special Studies: At the 15-month interim evaluation, plasma barium concentrations (mg/mL) were significantly increased in all exposed groups of mice (male: 0 ppm, 0.62; 500 ppm, 0.77; 1,250 ppm, 0.89; 2,500 ppm, 1.49; female: 0 ppm, 0.52; 500 ppm, 0.74; 1,250 ppm, 1.01; 2,500 ppm, 1.35). Pathology Findings: At the end of the 2-year study, there were increased incidences of nephropathy in male and female mice (male: 1/50, 0/50, 2/48, 19/50; female: 0/50, 2/53, 1/50, 37/54). There were no chemical-related increased incidences of neoplasms in male or female mice. The incidence of hepatocellular adenoma was significantly decreased in male mice receiving 2,500 ppm. GENETIC TOXICOLOGY: Barium chloride dihydrate was not mutagenic in Salmonella typhimurium strains TA97, TA98, TA100, TA1535, or TA1537, with or without exogenous metabolic activation (S9). It was mutagenic in L5178Y mouse lymphoma cells in the presence of S9, but it did not induce sister chromatid exchanges or chromosomal aberrations in cultured Chinese hamster ovary cells, with or without S9. CONCLUSIONS: Under the conditions of these 2-year drinking water studies, there was no evidence of carcinogenic activity of barium chloride dihydrate in male or female F344/N rats that received 500, 1,250, or 2,500 ppm. There was no evidence of carcinogenic activity of barium chloride dihydrate in male or female B6C3F1 mice that received 500, 1,250, or 2,500 ppm. There were chemical-related increased incidences of nephropathy in male and female mice.

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of C.I. Direct Blue 218 (CAS No. 28407-37-6) in F344/N Rats and B6C3F1 Mice (Feed Studies).

C.I. Direct Blue 218 is a copper chelated dye used for cellulose, acetate, nylon, silk, wool, tissue, papers, and textile goods with a urea-formaldehyde finish. C.I. Direct Blue 218 is one of five chemicals/dyes that are part of the National Toxicology Program's Benzidine Dye Initiative, established to determine the toxicity and carcinogenicity of representative benzidine congeners, congener-derived dyes, and benzidine-derived dyes. Industrial grade C.I. Direct Blue 218 was selected for study because of its widespread use. Because of the high salt content, the dye was desalted prior to use. Toxicology and carcinogenesis studies were conducted by administering C.I. Direct Blue 218 in feed to groups of male and female F344/N rats and B6C3F1 mice for 14 days, 13 weeks, and 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium, cultured Chinese hamster ovary cells, and Drosophila melanogaster. 14-DAY STUDY IN RATS: Groups of five male and five female F344/N rats were fed diets containing 0, 1,000, 3,000, 7,000, 15,000, or 30,000 ppm C.I. Direct Blue 218. All rats survived until the end of the study. Rats receiving 30,000 ppm lost weight, and the mean body weight gain of males receiving 15,000 ppm was significantly lower than that of the controls. Feed consumption by rats receiving 30,000 ppm was lower than that by the controls. Decreased organ weights at the 30,000 ppm level were related to the decreased body weights at this exposure level. 14-DAY STUDY IN MICE: Groups of five male and five female mice were fed diets containing 0, 1,000, 3,000, 7,000, 15,000, or 30,000 ppm C.I. Direct Blue 218. All mice survived until the end of the study. The final mean body weight of males receiving 30,000 ppm was 25% lower than that of controls and that of 30,000 ppm females was 20% lower than that of controls. Feed consumption by exposed and control groups was similar except for the 15,000 and 30,000 ppm groups. Feed spillage, due to reduced palatability, precluded the accurate determination of feed consumption by these two groups. Male and female mice receiving 30,000 ppm appeared hyperactive and emaciated during the last week of the study. Decreased organ weights were noted at 30,000 ppm and were attributed to the decreased mean body weights at this exposure level. 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female rats were fed diets containing 0, 3,000, 10,000, or 20,000 ppm C.I. Direct Blue 218. All male and female rats survived until the end of the study. Rats exposed to 3,000,10,000, or 20,000 ppm C.I. Direct Blue 218 received approximate daily doses of 200, 600 or 1,300 mg dye/kg body weight (males) and 200, 800, or 1,400 mg/kg (females). The final mean body weight of male rats receiving 20,000 ppm was 24% lower than that of the controls and the final mean body weight of female rats receiving 20,000 ppm was 15% lower than that of the controls. Feed consumption by exposed and control groups was similar except in the 20,000 ppm groups where feed spillage was noted. Absolute and relative kidney weights of rats receiving 10,000 or 20,000 ppm were significantly greater than those of controls. Significantly decreased organ weights were noted, particularly in the 20,000 ppm groups, and were attributed to the lower mean body weights at this exposure level. The hematocrit, hemoglobin, mean erythrocyte volume, and mean erythrocyte hemoglobin values in male and female rats receiving 10,000 and 20,000 ppm were significantly lower than those of controls. Serum levels of alanine aminotransferase and sorbitol dehydrogenase in male and female rats receiving 20,000 ppm were significantly higher than those of controls, which is consistent with hepatocellular injury. Male rats receiving 10,000 ppm and male and female rats receiving 20,000 ppm had hepatic lesions consisting of intracytoplasmic pigment in periportal Kupffer cells, minimal to mild individual hepatocyte necrosis, increased numbers of binucleated and multinucleated hepatocytes, and minimal bile duct hyperplasia. Male and female rats receiving 20,000 ppm had ys receiving 20,000 ppm had yellow-green pigment within the cytoplasm of proximal convoluted tubules of the kidney. Microconcretions of mineral were observed along the corticomedullary junction of the kidney in most female rats, but the numbers of microconcretions in kidney sections were increased in females that received 20,000 ppm. 13-WEEK STUDY IN MICE: Groups of 10 male and 10 female B6C3F1 mice were fed diets containing 0, 3,000, 10,000, or 20,000 ppm C.I. Direct Blue 218. There were no deaths attributed to C.I. Direct Blue 218. Mice exposed to 3,000, 10,000, or 20,000 ppm C.I. Direct Blue 218 received approximate daily doses of 400, 1,500, or 3,600 mg dye/kg body weight (males) and 400, 1,800, or 4,000 mg/kg (females). The final mean body weight of males that received 20,000 ppm was 24&percnt; lower than that of the controls, and the final mean body weight of females that received 20,000 ppm was 14&percnt; lower than that of controls. Feed consumption by exposed mice was similar to that by controls except in the 20,000 ppm groups where feed spillage was noted. Significant differences in organ weights were noted at 20,000 ppm which were attributed primarily to the lower mean body weights in these exposure groups. The hematocrit, hemoglobin, mean erythrocyte volume, and mean erythrocyte volume, and mean erythrocyte hemoglobin values were significantly lower in males and females receiving 10,000 and 20,000 ppm. Serum levels of alanine aminotransferase and sorbitol dehydrogenase in male and female mice receiving 10,000 and 20,000 ppm were significantly higher than those of controls, indicating hepatic injury. Male and female mice receiving 20,000 ppm had hepatic lesions consisting of centrilobular hepatocyte hypertrophy and karyomegaly, multifocal individual hepatocyte necrosis, oval cell proliferation, and periportal Kupffer cells with intracytoplasmic pigment. Males and females receiving 20,000 ppm also had increased numbers of pigmented macrophages within the red pulp of the spleen. 2-YEAR STUDY IN RATS: The doses selected for the 2-year study of C.I. Direct Blue 218 were based on the lower final mean body weights and the occurrence of hepatic lesions in the 20,000 ppm groups in the 13-week study. Groups of 60 male and 60 female rats were fed diets containing 0, 1,000, 3,000, or 10,000 ppm C.I. Direct Blue 218 for 103 weeks. Nine or 10 rats from each group were evaluated after 15 months. Survival, Body Weights, Feed and Compound Consumption, and Clinical Findings: Survival of female rats receiving 10,000 ppm was slightly, but not significantly, lower than that of the controls. Mean body weights of male and female rats in the 10,000 ppm groups were approximately 5&percnt; to 14&percnt; lower than those of the controls after week 15, and the final mean body weights of male and female rats at this level were 11&percnt; and 9&percnt; lower than those of the controls, respectively. Feed consumption by exposed male and female rats was similar to that by the controls and was estimated to deliver daily doses of 40, 120, and 440 mg dye/kg body weight to males and 50, 140, and 470 mg/kg to females. No chemical-related clinical signs of toxicity were noted. Hematology and Clinical Chemistry: The hematocrit, hemoglobin, mean erythrocyte volume, and mean erythrocyte hemoglobin values in 10,000 ppm female rats were significantly lower than those of controls, while in males only the mean erythrocyte hemoglobin value was significantly lower. Serum levels of alanine aminotransferase and sorbitol dehydrogenase in male and female rats receiving 10,000 ppm were significantly higher than those of the controls at the 15-month interim evaluation. Pathology Findings: Squamous cell papillomas of the oral mucosa (pharynx) occurred in five males receiving 10,000 ppm but not in the lower exposure groups or in controls. A squamous cell carcinoma occurred in one 10,000 ppm male and a benign basosquamous tumor was observed in another. The incidence of oral mucosal neoplasms in the 10,000 ppm males was significantly greater than that in controls and exceeded the range observed in untreated historical controls (lO/l,253, 0.8&percnt;; range 0&percnt;-4&percnt;). These neoplasms were considered chemical related. Administration of C.I. Direct Blue 218 to rats produced significantly increased incidences of forestomach basal cell hyperplasia in males receiving 3,000 or 10,000 ppm (0 ppm, 0/50; 1,000 ppm, 2/50; 3,000 ppm, 10/50;10,000 ppm, 19/50) and in females receiving 10,000 ppm (1/50, 1/49, 5/50, 11/49). Further, there were marginal increased incidences of focal squamous hyperplasia in the 3,000 and 10,000 ppm males (1/50,1/50, 6/50, 4/50). Squamous cell papillomas of the forestomach were seen in two 3,000 ppm males and in one 10,000 ppm male; no papillomas were observed in the controls. A squamous cell carcinoma was also seen in one 3,000 ppm male. Because of the uncommon occurrence of forestomach neoplasms in untreated control male rats (4/1,253, 0.3&percnt;; range 0&percnt;-2&percnt;) and the slight increase in the incidence of focal hyperplasia, these neoplasms may have been chemical related. The incidence of uterine endometrial stromal polyps in each exposed group of female rats was significantly greater than that of the controls (1/50,12/50,10/50, 10/50). Because the incidences in the exposed groups did not increase in a dose-related manner and the incidence in the controls was unusually low (historical incidence: 205/1,251,16.4&percnt;; range 2&percnt;-30&percnt;), the higher incidence of stromal polyps in the exposed groups was not considered chemical related. 2-YEAR STUDY IN MICE: The dose selection for the 2-year study was based on the lower final mean body weights and the liver lesions observed at the 20,000 ppm level in the 13-week study. Groups of 60 male and 60 female mice were fed diets containing 0, 1,000, 3,000, or 10,000 ppm C.I. Direct Blue 218 for 103 weeks. Nine or 10 mice from each exposure group were evaluated after 15 months. Survival, Body Weights, Feed and Compound Consumption, and Clinical Findings: Survival of exposed male and female mice was similar to that of the controls. Mean body weights of male and female mice receiving 10,000 ppm were 10&percnt; to 29&percnt; lower than those of the controls during most of the study, and the final mean body weights in these groups were 19&percnt; lower than that of the controls for males and 27&percnt; lower than that of the controls for females. Feed consumption by exposed mice was similar to that by controls and the diets were estimated to deliver daily doses of approximately 120, 360, and 1,520 mg of dye/kg body weight to males and 140, 470, and 2,050 mg/kg to females. No chemical-related clinical signs of toxicity were noted. Hematology and Clinical Chemistry: Hematocrit, hemoglobin, and mean erythrocyte volume values in males and females receiving 10,000 ppm were significantly lower than those of the controls. Serum levels of alanine aminotransferase and/or sorbitol dehydrogenase values in male and female mice that received 10,000 ppm were significantly higher than those of controls, which is consistent with hepatocellular damage. Pathology Findings: The administration of C.I. Direct Blue 218 to mice produced significantly increased incidences of hepatocellular adenoma (0 ppm, 16/50; 1,000 ppm, 19/50; 3,000 ppm, 17/50; 10,000 ppm, 40/50) and hepatocellular carcinoma (7/50, 3/50, 8/50,17/50) in males receiving 10,000 ppm, and a significantly increased incidence of hepatocellular adenoma in females receiving 3,000 or 10,000 ppm (7/49, 12/50, 17/49, 41/49). In females that received 10,000 ppm, the incidence of hepatocellular carcinoma was marginally increased. Consistent with these findings, the incidence of hepatocellular foci of cytologic alteration, a preneoplastic lesion, was also increased in males and females in the 10,000 ppm groups. The increased incidences of hepatocellular foci, adenomas, and carcinomas were considered chemical related. Uncommon renal tubule neoplasms also occurred at low incidences in male mice receiving C.I. Direct Blue 218, but not in controls. Renal tubule adenomas were seen in two males receiving 1,000 ppm, one male receiving 3,000 ppm, and one male receiving 10,000 ppm. A renal tubule carcinoma was also seen in one male that received 1,000 ppm. Because renal tubule neoplasms are uncommon in male mice (4/1,366, 0.3&percnt;; range 0&percnt;-2&percnt;), these neoplasms may have been chemical related. Carcinomas of the small intestine occurred in four male mice receiving 10,000 ppm. One was observed at the 15-month interim evaluation, while the other three were observed in mice at the end of the study. One control male mouse also had a carcinoma of the small intestine. Because of the uncommon occurrence of small intestine neoplasms in untreated male mice (12/1,374, 0.9&percnt;; range 0&percnt;-4&percnt;), the slightly higher incidence of these neoplasms in males receiving 10,000 ppm may have been chemical related. Carcinomas of the small intestine also occurred in one 3,000 ppm and one 10,000 ppm female, but the low incidences precluded drawing an association with chemical administration. GENETIC TOXICOLOGY: C.I Direct Blue 218 was not mutagenic in Salmonella typhimurium strains TA98, TA100, TA1535, or TA1537 tested with and without exogenous metabolic activation (S9). It was also tested in a modified Salmonella test protocol which employed reductive metabolism supplied by flavin mononucleotide or rat cecal bacteria, followed by oxidative metabolism; results of this test using strain TA1538 were also negative. C.I. Direct Blue 218 induced a small but significant increase in sister chromatid exchanges in Chinese hamster ovary cells at the highest dose tested without S9. No increase in chromosomal aberrations were observed in Chinese hamster ovary cells with or without S9. C.I. Direct Blue 218 did not induce sex-linked recessive lethal mutations in germ cells of male Drosophila melanogaster. CONCLUSIONS: Under the conditions of these 2-year feed studies, there was some evidence of carcinogenic activity of C.I. Direct Blue 218 in male F344/N rats based on the occurrence of pharyngeal neoplasms. Squamous cell neoplasms of the forestomach may have been chemical related. There was no evidence of carcinogenic activity of C.I Direct Blue 218 in female F344/N rats given 1,000, 3,000, or 10,000 ppm. There was clear evidence of carcinogenic activity of C.I. Direct Blue 218 in male and female B6C3F1 mice based on increased incidences of hepatocellular adenomas and carcinomas. The occurrence of a few neoplasms of the kidney and small intestine in male mice may have been related to C.I. Direct Blue 218 treatment. The administration of C.I. Direct Blue 218 produced an increased incidence of forestomach basal cell hyperplasia in rats and hepatocellular foci of cytologic alteration in mice. Synonyms: cuprate(4-), [mu-[(3,3'-dihydroxy[1,1'-biphenyl]-4,4'-diyl)bis[5-amino-4-hydroxy- 2,7-naphthalnedisulfonato]](8-)]]di-, tetrasodium; copper, [tetrahydrogen-3,3'-[(3,3'-dihydroxy-4,4'-biphenylylene)bis(azo)]bis [5-amino-4-hdroxy-2,7-naphthalenedisulfonato](4-)]di-, tetrasodium salt; 1-naphthol-3,6-disulfonic acid, 2,2'-(3,3'-dihydroxy-4,4'-biphenylylenebisazo)bis [8-amino-, dicopper deriv., tetrasodium salt

Journal Article↗

NTP Comparative Toxicology Studies of Corn Oil, Safflower Oil, and Tricaprylin (CAS Nos. 8001-30-7, 8001-23-8, and 538-23-8) in Male F344/N Rats as Vehicles for Gavage.

The types and levels of fats in the diet are known to affect the incidence of certain neoplasms in humans and rodents. In long-term toxicity and carcinogenicity studies in rodents, the level of dietary fat is altered by using oil as a vehicle to administer unpalatable or volatile chemicals. Control male rats receiving a corn oil vehicle have a higher incidence of pancreatic proliferative lesions and a lower incidence of mononuclear cell leukemia than untreated control males. Therefore, the National Toxicology Program (NTP) designed studies to evaluate the role of several oils in altering cancer rates in male rats. The NTP study reported here was part of a larger program that included cooperative agreements with Dartmouth Medical School, Northwestern Medical School, and the University of Missouri. The program was designed to study the mechanisms by which corn oil induces pancreatic cancer. To evaluate corn oil as well as two other gavage vehicles for potential toxicity, corn oil, safflower oil, and tricaprylin were administered by gavage to male F344/N rats for 2 years. The rats that received corn oil were also made available to the university investigators for study of the corn oil-induced pancreatic lesions. Each vehicle was administered by gavage at volumes of 2.5, 5, or 10 mL/kg body weight once daily for 5 days per week. In the corn oil study, a control of 10 mL saline/kg was also included. To evaluate the potential role of corn oil in promoting a pancreatic proliferative effect, 500 mg dichloromethane/kg body weight was administered in 2.5, 5, or 10 mL corn oil/kg body weight for 2 years to male F344/N rats. Dichloromethane was chosen because the chemical appeared to cause pancreatic proliferative lesions when administered by gavage in a corn oil vehicle but not when the exposure was by inhalation. In each of these studies, the term "dose" refers to the volume of gavage vehicle administered. 2-YEAR STUDIES OF CORN OIL, SAFFLOWER OIL, AND TRICAPRYLIN: Survival and Body Weights: Two-year survival was increased in male rats receiving corn oil (untreated control, 26/50; saline control, 32/50; 2.5 mL/kg, 33/50; 5 mL/kg, 38/50; 10 mL/kg, 40/50) primarily due to a dose-related decreased incidence of mononuclear cell leukemia. The mean body weights of all dosed groups were at least 5% higher than those of the untreated and saline controls by week 48, but the mean body weights of groups receiving 2.5 or 5 mL corn oil/kg decreased during the final weeks of the study (after week 89) and were similar to those of the controls at the end of the study. Two-year survival was slightly increased in male rats receiving safflower oil relative to that of the controls (untreated control, 30/50; 2.5 mL/kg, 33/50; 5 mL/kg, 40/50; 10 mL/kg, 36/50). The mean body weight of male rats receiving 10 mL safflower oil/kg was at least 5% greater than that of the controls after week 45 and was 16% greater by the end of the study. Two-year survival of high-dose tricaprylin males was lower than that of the controls (untreated control, 31/50; 2.5 mL/kg, 30/50; 5 mL/kg, 31/50; 10 mL/kg, 23/53) due to moribund kills and deaths that appeared to be related to toxicity. The mean body weight of the high-dose group was lower than that of the controls throughout the study, although the difference was less than 5% after week 61. Pathology Findings: In the corn oil study, there were significant dose-related increased incidences of pancreatic exocrine hyperplasia and adenoma (hyperplasia: 8/50, 28/47, 28/50, 35/50; adenoma: 1/50, 8/47, 10/50, 23/50; carcinoma: 0/50, 0/47, 1/50, 0/50 in the untreated control, 2.5, 5, and 10 mL/kg groups, respectively). The incidence and severity of nephropathy decreased with dose (incidence [mean severity grade]: 47/50 [2.1], 43/48 [1.8], 45/50 [1.4], 40/49 [1.2]). The incidences of pheochromocytomas (benign, malignant, or complex) of the adrenal medulla were also decreased in dosed rats (23/49, 21/50, 5/50, 9/50). The incidence of mononuclear cell leukemia was significantly decreased in rats dosed with corn oil (27/50, 16/50, 11h corn oil (27/50, 16/50, 11/50, 7/50). In rats receiving safflower oil, the incidences of pancreatic exocrine hyperplasia and adenoma increased significantly with dose (hyperplasia: 8/50, 14/50, 29/49, 30/50; adenoma: 1/50, 7/50,15/49, 28/50; carcinoma: 0/50, 0/50, 0/49, 1/50 in the untreated control, 2.5, 5, and 10 mL/kg groups, respectively). There was a decrease in the severity, but not in the incidence, of nephropathy, a common lesion in aging F344/N rats (incidence [mean severity grade]: 49/50 [2.0], 50/50 [1.8], 47/50 [1.1], 49/49 [1.1]). There were decreased incidences of mononuclear cell leukemia (33/50, 19/50, 18/50, 7/51). In the tricaprylin study, there were significant dose-related increased incidences of pancreatic exocrine hyperplasia and adenoma (hyperplasia: 8/49, 9/49, 18/49, 28/50; adenoma: 2/49, 6/49,13/49,18/50 in the untreated control, 2.5, 5, and 10 mL/kg groups, respectively). The incidence of proliferative lesions of the forestomach increased significantly with dose (basal cell hyperplasia: 4/50, 7/50, 12/49, 21/52; squamous cell papilloma: 0/50, 0/50, 3/50, 10/53). The incidence of nephropathy was significantly decreased in high-dose rats, and the severity of nephropathy decreased with dose (incidence [mean severity grade]: 46/50 [2.0], 42/50 [1.5], 45/50 [1.7], 27/49 [0.9]). In high-dose rats, the incidence of mononuclear cell leukemia was decreased (23/50, 28/50, 22/50, 9/53). 2-YEAR STUDY OF DICHLOROMETHANE IN CORN OIL: Survival and Body Weights: Two-year survival increased slightly with dose in the three groups receiving 500 mg dichloromethane/kg in 2.5, 5, or 10 mL corn oil/kg (23/50, 28/50, 31/50) due to a dose-related decrease in the incidence of mononuclear cell leukemia. The rats receiving 500 mg dichloromethane/kg without corn oil were sacrificed within the first 3 weeks of the study due to the severe toxicity of dichloromethane. The final mean body weight of the high-dose rats was greater than the final mean body weights of groups receiving dichloromethane in 2.5 or 5 mL corn oil/kg. Pathology Findings: There was a dose-related increase in the incidence of pancreatic proliferative exocrine lesions in rats receiving dichloromethane in 2.5, 5, and 10 mL corn oil/kg (hyperplasia: 28/50, 38/50, 44/50; adenoma: 9/50,19/50, 41/50; carcinoma: 0/50,1/50, 3/50). The incidences of pancreatic exocrine hyperplasia and adenoma in rats receiving dichloromethane in 5 or 10 mL, but not 2.5 mL, corn oil were increased compared to the incidences in rats receiving comparable volumes of corn oil alone (hyperplasia: 2.5 mL, 28/47; 5 mL, 28/50;10 mL, 35/50; adenoma: 8/47,10/50, 23/50; carcinoma: 0/47,1/50, 0/50). There were significantly increased incidences of pituitary gland pars distalis adenoma in rats receiving dichloromethane in corn oil (20/50, 18/49, 16/49) when compared to those in rats receiving comparable volumes of corn oil alone (10/50, 6/49, 7/50). The incidence of mammary gland adenoma and fibroadenoma (combined) was significantly increased in rats receiving dichloromethane in 10 mL corn oil/kg (7/50) when compared to rats receiving dichloromethane in 2.5 mL corn oil/kg (1/50), but was not significantly increased when compared to the group receiving 10 mL of corn oil alone (3/50). The incidences of mammary gland adenoma and fibroadenoma (combined) were 7/50 for the untreated safflower oil controls and 6/50 for the untreated tricaprylin controls. The incidence of mononuclear cell leukemia decreased in the group receiving dichloromethane in 10 mL corn oil/kg (13/50,14/50, 5/50). GENETIC TOXICOLOGY: Neither safflower oil nor corn oil was mutagenic in Salmonella typhimurium strains TA97, TA98, TA100, or TA1535, with or without S9. Tricaprylin, in contrast, was mutagenic in strain TA1535 with, but not without, S9. Tricaprylin did not induce mutations in strains TA97, TA98, or TA100, with or without S9. SUMMARY: These studies were designed to evaluate the effects of various concentrations of an oil very high in polyunsaturated fat (safflower oil), an oil containing high levels of polyunsaturated and monounsaturated fats (corn oil), and an oil containing saturated medium-chain fatty acids (tricaprylin) on the incidence and pattern of neoplasms in the F344/N rat. In addition, safflower oil and tricaprylin were evaluated as replacements for the corn oil vehicle. These studies demonstrate that safflower oil and tricaprylin do not offer significant advantages over corn oil as a gavage vehicle in long-term rodent studies. Corn oil, safflower oil, and tricaprylin each caused hyperplasia and adenoma of the exocrine pancreas, decreased incidences of mononuclear cell leukemia, and reduced incidences or severity of nephropathy in male F344/N rats. There was an increased incidence of squamous cell papillomas of the forestomach in F344/N rats receiving 10 mL tricaprylin/kg. Further, the use of corn oil as a gavage vehicle may have a confounding effect on the interpretation of chemical-induced proliferative lesions of the exocrine pancreas and mononuclear cell leukemia in male F344/N rats. Synonyms: Corn Oil - Maize oil, Maydol Tricaprylin - Trioctanoin; 1,2,3-trioctanoyl glycerol; Glycerol trioctanoate

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of 2,3-Dibromo-1-Propanol (CAS No. 96-13-9) in F344/N Rats and B6C3F1 Mice (Dermal Studies).

2,3-Dibromo-l-propanol, a colorless liquid, has been used as a flame retardant, as an intermediate in the preparation of the flame retardant tris(2,3-dibromopropyl) phosphate, and as an intermediate in the manufacture of pesticides and pharmaceutical preparations. Toxicology and carcinogenicity studies were conducted by applying 2,3-dibromo-1-propanol (approximately 98% pure) in ethanol to the subscapular area of the skin of male and female F344/N rats and B6C3F1 mice 5 days per week for 16 days, 13 weeks, 48 to 51 weeks (male rats), 52 to 55 weeks (female rats), 36 to 39 weeks (male mice), or 39 to 42 weeks (female mice). Genetic toxicology studies were conducted in Salmonella typhimurium, cultured Chinese hamster ovary cells, Drosophila melanogaster, mouse Iymphoma cells, and mouse bone marrow cells. 16-DAY STUDY IN RATS Groups of five male and five female rats received dermal applications of 0, 44, 88, 177, 375, or or 750 mg/kg 2,3-dibromo-1-propanol 5 days per week for 16 days. One male and one female receiving 750 mg/kg died before the end of the study. The mean body weight gains and final mean body weights of dosed rats were similar to those of the controls. There were no clinical findings or gross lesions associated with chemical application. 16-DAY STUDY IN MICE Groups of five male and five female mice received dermal applications of 0, 44, 88, 177, 375, or 750 mg/kg 2,3-dibromo-1-propanol 5 days per week for 16 days. Four males and one female receiving 750 mg/kg died before the end of the study. The mean body weight gains and final mean body weights of dosed mice were similar to those of the controls. There were no clinical findings or gross lesions associated with chemical application. 13-WEEK STUDY IN RATS Groups of 10 male and 10 female rats received dermal applications of 0, 44, 88, 177, 375, or 750 mg/kg 2,3-dibromo-1-propanol 5 days per week for 13 weeks. All rats survived until the end of the for 16 days. One male and one female receiving study. For rats in the 750 mg/kg groups, the mean 750 mg/kg died before the end of the study. The body weight gain was 11% lower than that of the controls for males and 13% lower for females. The mean liver weights and liver-weight-to-body-weight ratios of males receiving 375 or 750 mg/kg and of females receiving 750 mg/kg were increased. Chemical-related lesions occurred in the kidney of male rats and in the liver of female rats. The average severity of nephropathy was slightly increased in males receiving dermal applications of 750 mg/kg, while individual cell necrosis was observed in the liver of all female rats in the 750 mg/kg group. 13-WEEK STUDY IN MICE Groups of 10 male and 10 female mice received dermal applications of 0, 44, 88, 177, 375, or 750 mg/kg 2,3-dibromo-1-propanol 5 days per week for 13 weeks. Eight male mice receiving 750 mg/kg died during the study, while all female mice survived. The final mean body weights of dosed and control mice were similar. The mean liver weights and liver weight-to-body-weight ratios of males receiving 375 or 750 mg/kg and of females receiving 750 mg/kg were increased. Chemical-related lesions occurred in the liver and lung of mice. Centrilobular hepatocellular necrosis occurred in all males in the 750 mg/kg group that died during the study, while individual cell necrosis was observed in the liver of females receiving 177, 375, or 750 mg/kg. Pleomorphism of the epithelium in pulmonary bronchioles occurred with a dose related increased incidence in males and females. Necrosis of the bronchiolar epithelium was observed in males receiving 750 mg/kg. LONG-TERM STUDY IN RATS Originally planned to last for 2 years, the chronic study in rats was terminated early because of reduced survival in the high-dose groups related to chemical induced neoplasms and because of the detection of antibodies to Iymphocytic choriomeningitis virus in sentinel mice. Groups of 50 male and 50 female rats received dermal applications of 0,188, or 375 mg/kg 2,3-dibromo-1-propanol 5 days per week for 48 to 51 weeks (males) or 52 to 55 weeks (females). Su5 weeks (females). Survival, Body Weights, and Clinical Findings The survival of 375 mg/kg male and female rats was significantly lower than that of the controls (males: 50/50, 41/50,16/50; females: 48/50, 38/50, 24/50). In the 375 mg/kg groups, the final mean body weight was 23&percnt; lower than that of the controls for males and 14&percnt; lower for females. There were no chemical related clinical findings. Pathology Findings Application of 2,3-dibromo-1-propanol to the skin produced significant dose-related increases in the incidences of neoplasms at numerous sites in male and female rats. Almost all dosed rats had malignant neoplasms; only one control male and one control female had malignant neoplasms. In male rats, the incidences of benign or malignant neoplasms of the skin, nose, Zymbal's gland, oral mucosa, esophagus, and small and large intestines were significantly increased in the low- and high-dose groups, while the incidences of neoplasms of the forestomach and liver were significantly increased only in the high-dose group. Neoplasms of the kidney, vascular neoplasms of the spleen, and mesotheliomas in males occurred with a significant positive trend. In female rats, the incidences of benign or malignant neoplasms of the nose, Zymbal's gland, oral mucosa, esophagus, large intestine, and liver were significantly increased in the low- and high-dose groups, while the incidences of neoplasms of the skin, forestomach, small intestine, mammary gland, and clitoral gland were significantly increased in the high-dose group only. Neoplasms of the kidney in females occurred with a significant positive trend. LONG-TERM STUDY IN MICE Originally planned to last for 2 years, the chronic study in mice was terminated early because of the detection of antibodies to lymphocytic choriomeningitis virus in sentinel mice. Groups of 50 male and 50 female mice received dermal applications of 0, 88, or 177 mg/kg 2,3-dibromo-1-propanol 5 days per week for 36 to 39 weeks (males) or 39 to 42 weeks (females). Survival, Body Weights, and Clinical Findings All mice (except two low-dose females) survived until study termination. Mean body weights of control and dosed mice were similar throughout the study, and there were no clinical findings attributed to 2,3-dibromo-l-propanol. Pathology Findings Application of 2,3-dibromo-1-propanol to the skin produced significant dose-related increases in the incidences of neoplasms at several sites in male and female mice. Benign or malignant neoplasms were observed in 40&percnt; of the low-dose males, 66&percnt; of the high-dose males, 52&percnt; of the low-dose females, and 56&percnt; of the high-dose females. In control groups, neoplasms occurred in 6&percnt; of the males and 10&percnt; of the females. In male and female mice, the incidences of benign or malignant neoplasms of the forestomach were significantly increased in the low- and high-dose groups, while the incidences of neoplasms of the skin were significantly increased only in the high-dose groups. The incidences of liver and lung neoplasms were increased in high-dose males. GENETIC TOXICOLOGY 2,3-Dibromo-l-propanol was mutagenic in a variety of short-term tests, independent of exogenous metabolic activation (S9). It induced gene mutations in three strains of Salmonella typhimurium (TA98, TA100, and TA1535) and was positive in the mouse Iymphoma assay for induction of trifluorothymidine resistance in L5178Y cells. 2,3-Dibromo-l-propanol induced sister chromatid exchanges and chromosomal aberrations in cultured Chinese hamster ovary cells. In germ cells of male Drosophila melanogaster, 2,3-dibromo-1-propanol induced sex-linked recessive lethal mutations and reciprocal translocations. Results of an in vivo bone marrow micronucleus assay in male mice treated with 2,3-dibromo-1-propanol were negative. CONCLUSIONS Under the conditions of these long-term dermal studies, there was clear evidence of carcinogenic activity of 2,3-dibromo-1-propanol in male F344/N rats based on increased incidences of neoplasms of the skin, nose, oral mucosa, esophagus, forestomach, small and large intestine, Zymbal's gland, liver, kidney, tunica vaginalis, and spleen. There was clear evidence of carcinogenic activity of 2,3-dibromo-1-propanol in female F344/N rats based on increased incidences of neoplasms of the skin, nose, oral mucosa, esophagus, forestomach, small and large intestine, Zymbal's gland, liver, kidney, clitoral gland, and mammary gland. There was clear evidence of carcinogenic activity of 2,3-dibromo-1-propanol in male B6C3F1 mice based on increased incidences of neoplasms of the skin, forestomach, liver, and lung. There was clear evidence of carcinogenic activity of 2,3-dibromo-1-propanol in female B6C3F1 mice based on increased incidences of neoplasms of the skin and the forestomach. The increased incidences of alveolar/bronchiolar adenomas in female mice may have been related to chemical administration. In rats, 2,3-dibromo-1-propanol caused increased incidences of hyperkeratosis in the skin, forestomach, and esophagus, epithelial dysplasia in the nose, pleomorphism and basophilic and clear cell changes in the liver, and nuclear enlargement in the kidney. There were also chemical-related increases in the incidences of forestomach ulcers and acanthosis, angiectasis in the liver, and renal hyperplasia in male rats and epithelial dysplasia of the forestomach and bile duct hyperplasia in the liver in female rats. Chemical-related increases occurred in the incidences of hyperplasia in the skin, epithelial dysplasia of the forestomach, and bronchiolar epithelial pleomorphism and hyperplasia in male and female mice and in the incidence of eosinophilic cytoplasmic change in the liver in males. Synonyms: 2,3-dibromopropanol; 2,3-dibromopropyl alcohol.

Journal Article↗

NTP Toxicology and Carcinogenesis Studies of Oxazepam (CAS No. 604-75-1) in Swiss-Webster and B6C3F1 Mice (Feed Studies).

Oxazepam is one of a number of benzodiazepines used therapeutically as a sedative-hypnotic and antianxiety agent. Toxicology and carcinogenesis studies were performed by administering oxazepam (greater than 99% pure) in feed to male and female Swiss-Webster and B6C3F1 mice for 14 weeks, 57 weeks (Swiss-Webster), or 2 years (B6C3F1). Neurobehavioral assessments were performed during the studies. Genetic toxicology studies were conducted in Salmonella typhimurium and cultured Chinese hamster ovary cells, and peripheral blood samples were analyzed for frequency of micronucleated normochromatic erythrocytes. Supplemental studies were performed to compare the metabolism and toxicokinetics of oxazepam in the two mouse strains, to evaluate the effect on liver cell replication rates, to perform clinical pathology assessments, and to examine the mutation spectrum and frequency of activated H-ras oncogenes in liver neoplasms from the 2-year study with B6C3F1 mice. 14-WEEK STUDY IN SWISS-WEBSTER MICE: Groups of 10 male and 10 female Swiss-Webster mice received oxazepam in feed at concentrations of 0, 625, 1,250, 5,000, 10,000 ppm for 14 weeks. One 625 ppm male and one 10,000 female were killed moribund before the end of the study, and the condition of the female mouse was attributed to oxazepam exposure. Mean body weight gains of exposed groups were similar to those of the controls. Exposed mice displayed chemical-related sedation and lethargy during the first study week, but appeared normal thereafter. In the neurobehavioral studies, reductions in grip strength were evident in both male and female mice at week 2 and persisted in males through week 11. An antianxiety effect was detected in exposed mice in measures of motor activity, startle response, and reactions to thermal stimulus. At necropsy, absolute and relative liver weights were increased in an exposure-related manner and were approximately two-fold greater in 10,000 ppm mice than in controls. Centrilobular hepatocellular hypertrophy was present only in exposed mice, and the severity increased with dose. 14-WEEK STUDY IN B6C3F1 MICE: Groups of 10 male and 10 female B6C3F1 mice received oxazepam in feed at concentrations of 0, Groups of 10 male and 10 female Swiss-Webster mice 625, 1,250, 2,500, 5,000, or 10,000 ppm for 14 weeks. received oxazepam in feed at concentrations of 0, There were no deaths that were clearly related to 625,1,250, 2,500, 5,000, or 10,000 ppm for 14 weeks. oxazepam exposure. Mean body weight gains of One 625 ppm male and one 10,000 ppm female were exposed groups were similar to those of the controls. Exposed mice displayed chemical-related sedation and lethargy during only the first study week. In neurobehavioral studies, reductions in grip strength were evident in males at week 2 but were no longer observed at week 12. An antianxiety effect was noted in exposed mice in measures of motor activity, startle response, and reactions to a thermal stimulus (females). At necropsy, absolute and relative liver weights were increased in an exposure-related manner and were approximately two-fold greater in 10,000 ppm mice than in controls. Centrilobular hepatocellular hypertrophy was present only in exposed mice, and the severity increased with dose. CHRONIC STUDIES: Groups of 60 male and 60 female Swiss-Webster and B6C3F1 mice received oxazepam in feed at concentrations of 0, 2,500, or 5,000 ppm. Additional groups of 60 male and 60 female B6C3F1 mice received 125 ppm in feed to allow for study of a group with projected serum concentrations of oxazepam similar to those achieved in humans taking a therapeutic dose. Ten male and 10 female B6C3F1 mice per group were evaluated at 15 months. Average daily oxazepam consumption varied throughout the studies, and the overall daily average ranged from 10 to 29 mg/kg body weight for the 125 ppm groups, 234 to 512 mg/kg for the 2,500 ppm groups, and 444 to 1,085 mg/kg for the 5,000 ppm groups. Serum oxazepam concentrations determined at 57 weeks in Swiss-Webster mice and at the 15-month interim evaluation of B6C3F1 mice 1 mice were approximately 1 ug/mL in the 125 ppm groups, 4 to 7 &mu;g/mL in the 2,500 ppm groups, and 7 to 10 &mu;g/mL in the 5,000 ppm groups. Neurobehavioral assessments during the chronic studies of each strain of mice were confounded by the poor survival and deteriorating condition of mice with hepatic neoplasia. However, within the limitations of the studies, there were no notable changes in the types of behaviors observed compared to those observed in the 14-week studies, nor was there an enhancement in the degree to which they were exhibited. 57-Week Study in Swiss-Webster Mice: Survival, Body Weights, Feed and Compound Consumption, and Clinical Findings: At 57 weeks, survival of exposed mice was significantly lower than that of controls (males: O ppm, 45/60; 2,500 ppm, 19/60; 5,000 ppm, 10/60; females: 47/60, 28/59, 17/59), causing the study to be terminated. Mean body weights of exposed males were similar to controls until week 17; afterwards, mean body weights of exposed male groups were lower than those of controls. Final mean body weights of exposed males were 9% lower than that of the controls. The mean body weight of 2,500 ppm females was greater than that of the controls throughout the study. Females receiving 5,000 ppm had a mean body weight greater than that of the controls early in the study; after week 29, the mean body weight of this group was similar to that of the controls. Feed consumption by exposed males and females was slightly lower than that by the controls, and females in all groups, including controls, consumed slightly more feed than males throughout the study. Dietary levels of 2,500 and 5,000 ppm oxazepam resulted in average daily compound consumption levels of 270 and 570 mg/kg for males and 320 and 670 mg/kg for females. Hypoactivity and sedation were observed in exposed mice during the first week of the study. There were no other clinical findings associated with oxazepam exposure. Pathology Findings: Systemic amyloidosis was the principal cause of death in mice dying before the study was terminated. The lower survival of mice receiving oxazepam was attributed to an increase in the extent and severity of amyloid deposits in many organs, including the heart and kidney. Atrial thrombosis and pulmonary lesions consistent with chronic heart failure occurred at higher incidences and with greater severity in exposed mice. The incidence of hepatocellular adenomas (males: 1/60, 35/60, 50/60; females: 0/60, 22/59, 47/59) and carcinomas (males: 0/60, 5/60,19/60; females: 1/60, 1/59, 11/59) were increased in exposed mice. The incidences of eosinophilic foci were also increased in exposed mice (males: 0/60, 22/60, 22/60; females: 0/60, 20/59, 14/59), and there was evidence of increased centrilobular hepatocyte hypertrophy (males: 12/60, 46/60, 47/60; females: 3/60, 51/59, 53/59). 2-Year Study in B6C3F1 Mice: Survival, Body Weights, Feed and Compound Consumption, and Clinical Findings: Survival of mice receiving 2,500 and 5,000 ppm was significantly lower than that of controls (males: O ppm, 45/50; 125 ppm, 44/50; 2,500 ppm, 15/50; 5,000 ppm, 0/50; females: 39/50, 41/50, 2/50, 0/50). Mean body weight gains of exposed male and female mice were similar to controls until about week 15 when weight gains for mice exposed to 2,500 or 5,000 ppm slowed in relation to controls, resulting in weight gains approximately 30&percnt; to 40&percnt; lower than those of the controls throughout the remainder of the study. Mean body weight gain of male mice exposed to 125 ppm was similar to that of the controls, while that of female mice receiving 125 ppm was 10&percnt; to 15&percnt; lower than that of the controls after about week 45. Feed consumption by exposed males and females was similar to that by controls. Dietary levels of 125, 2,500, and 5,000 ppm resulted in average daily oxazepam consumption levels of 12, 310, and 690 mg/kg body weight for males and 15, 350, and 780 mg/kg for females. In the 5,000 ppm groups, lethargy and sedation were observed in a few mice during the first week of study. Pathology Findings: The early deaths of many of the B6C3F1 mice exposed to oxazepam were attributed to a marked increase in the incidences of hepatoblastoma (males: 0/49, 2/50, 21/50, 13/50; females: 0/50, 1/50, 8/50, 8/50), hepatocellular adenoma (males: 17/49,18/50, 34/50, 32/50; females: 25/50, 35/50, 35/50, 36/50), and hepatocellular carcinoma (males: 9/49, 5/50, 45/50, 50/50; females: 9/50, 5/50, 49/50, 44/50). Moderate hypertrophy of centrilobular hepatocytes occurred in mice receiving 2,500 and 5,000 ppm (males: 0/49, 2/50, 26/50, 43/50; females: 0/50, 2/50,11/50, 29/50). An increase in the incidence of follicular cell hyperplasia of the thyroid gland occurred in all exposed groups of mice (males: 4/49, 22/50, 49/50, 47/50; females: 16/50, 34/50, 49/50, 44/50), and thyroid gland follicular cell adenoma was increased in exposed females (0/50, 4/50, 5/50, 6/50). Testicular atrophy occurred in the 2,500 and 5,000 ppm groups (1/50, 0/50, 25/50, 38/50), and the incidence of epididymal Iymphocyte infiltration was increased in all exposed groups (2/50,14/50, 33/50, 21/50). The frequency of hepatocellular neoplasms with an activated H-ras oncogene in the B6C3F1 mice and the mutation spectrum of the H-ras gene were determined. The mutation spectrum of the H-ras genes in the relatively few neoplasms from exposed mice that did have an activated H-ras did not differ from the spectrum of mutations observed in neoplasms from controls, but the proportion of neoplasms with an activated H-ras gene decreased with increasing oxazepam dose. While 11 of 19 (58&percnt;) neoplasms from control mice had an activated H-ras gene, only 1 of 40 neoplasms from mice receiving 2,500 or 5,000 ppm oxazepam exhibited a similar molecular lesion. Thirteen of 37 (35&percnt;) neoplasms from mice in the 125 ppm group had an activated H-ras oncogene, suggesting that, although the incidence of all liver neoplasms was not statistically increased compared to controls, there was an increase in a similar subset of neoplasms (lacking an activated H-ras) that occurred with increased incidence at higher doses. SUPPLEMENTAL STUDIES: Because exposure to oxazepam caused increased incidences of liver neoplasms, supplemental short-term studies were performed. Oxazepam given in feed to male B6C3F1 mice at 25, 125, 2,500, or 5,000 ppm for up to 13 weeks was found to cause a dose-related increase in nuclear labeling index in studies measuring the incorporation of bromodeoxyuridine into replicating liver cells. This increase was statistically significant at all but the 25 ppm exposure level and was limited to mice evaluated at 15 days. Cell replication rates in most groups evaluated at 30 days and after were similar to control rates. There was minimal evidence suggestive of hepatocyte necrosis either by light microscopy or in clinical chemistry measures. There was, however, evidence of cholestasis, likely due to physical obstruction of bile canaliculi by swollen hepatocytes. The metabolic fate and toxicokinetics of oxazepam were evaluated in each strain of mice and were compared to published data from human studies. Both mice and humans form glucuronides of oxazepam and form 3- and 4-hydroxy and methoxy derivatives of the phenyl group. Oxidative metabolism of the phenyl group appears to be more prevalent in mice than is reported for humans. Elimination half-lives of parent compound do not differ between Swiss-Webster and B6C3F1 mice and are similar to values reported for humans. GENETIC TOXICOLOGY: Oxazepam was not mutagenic in any of several strains of Salmonella typhimurium, nor did it induce sister chromatid exchanges or chromosomal aberrations in cultured Chinese hamster ovary cells. These in vitro tests were performed with and without S9 metabolic activation. Results from an in vivo mouse peripheral blood micronucleus test performed on the B6C3F1 mice used in the 14-week study were also negative. CONCLUSIONS: Under the conditions of these feed studies, there was clear evidence of carcinogenic activity of oxazepam in male and female Swiss-Webster mice based on increased incidences of hepatocellular adenoma and carcinoma. There was clear evidence of carcinogenic activity of oxazepam in male and female B6C3F1 mice based on increased incidences of hepatoblastoma and hepatocellular adenoma and carcinoma. Increased incidences of hyperplasia of thyroid gland follicular cells in male and female B6C3F1 mice and of follicular cell adenomas in female B6C3F1 mice were also related to oxazepam exposure. Administration of oxazepam to Swiss-Webster mice resulted in centrilobular hepatocellular hypertrophy and increased incidences and severity of systemic amyloidosis. Administration of oxazepam to B6C3F1 mice also resulted in centrilobular hepatocellular hypertrophy. Synonyms: 7-Chloro-1,3-dihydro-3-hydroxy-5-phenyl-2 H - 1,4-benzodiazepin-2-one Trade Names: Tazepam, Wy-3498, Serax

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