Inhalation toxicity of dimethyl piperidinone.

A mixture of 1,3-dimethyl-2-piperidinone and 1,5-dimethyl-2-piperidinone (DMPD) (approximately 63-37 parts by weight) was tested for its inhalation toxicity in rats following 90-day repeated exposures. Male and female rats were exposed whole-body to either 0, 51, 230, or 310 mg/m(3) DMPD for 6 h/day, 5 days/weak for 90 days. Clinical signs, growth, clinical pathology, tissue pathology, neurobehavior, neuropathology, and semen quality were evaluated. No compound-related adverse effects were noted in clinical signs, body weights, food consumption, clinical laboratory evaluations, neurobehavioral evaluations, neuropathology, or sperm counts. Laryngeal changes consisting of minimal squamous epithelial hyperplasia and degeneration/necrosis of the cartilage were present in male and female rats exposed to 310 mg/m(3) both immediately following exposure and after the 1-month recovery period Male rats exposed to DMPD had increased relative kidney weights, increased formation of hyaline droplets and granular casts, and increased incidence of chronic progressive nephropathy. These kidney effects are consistent with increased accumulation of the urinary protein alpha(2 mu)-globulin, which has been well essential for several xenobiotics. The subsequent increased incidence of progressive nephropathy was specific to male rats with the alpha(2 mu) syndrome. Male and female rats exposed to 230 or 310 mg/m(3) had centrilobular hepatocellular hypertrophy, and male rats exposed to 310 mg/m(3) had increased relative liver weights. These liver changes were reversible following the recovery period and were considered not to represent adverse toxicological effects of treatment. Since the male rat-specific renal findings do not connote adversity for man and are net considered relevant to human hazard assessment, the no-observed-effect level in male and female rats was 230 mg/m(3), based on the microscopic changes in the larynx exposed to 310 mg/m(3).

Inhalation toxicity of tetramethylurea in rats.

Tetramethylurea (TMU, CAS No. 632-22-4) was tested for its inhalation toxicity in rats following repeated exposures. Male rats were exposed whole-body to TMU for 6 hours/day, 5 days/week for a total of 9 exposures over 2 weeks. Concentrations of 0 (control), 2, 20, and 100 ppm were studied. Four groups of 10 rats each were used to measure clinical signs and growth, clinical pathology (including hematology, biochemistries, and urine analysis), and tissue pathology. One-half of the rats were sacrificed 1 day following the 9th exposure; the other half underwent an 18-day recovery period prior to being sacrificed (recovery group). Body weight gains in rats exposed to 100 ppm were reduced as compared to the controls; no body weight effects were seen in either 2 or 20 ppm rats and no clinical signs of toxicity were observed in rats at any of the levels throughout the study. No compound-related clinical pathology changes were seen in any of the test groups and tissue pathology effects only occurred in the nasal tissue. In rats exposed to 100 ppm, microscopic observations of degeneration, necrosis, and ulceration of olfactory mucosa was seen. These lesions were still present but seen as recovering and healing after the 18-day recovery. Under the conditions of this test, the no-observed-adverse-effect level (NOAEL) was determined to be 20 ppm based upon both body weight changes and upper respiratory tract pathologic changes in 100 ppm rats.

Chronic toxicity and oncogenicity of N-methylpyrrolidone (NMP) in rats and mice by dietary administration.

A two-year feeding study in rats and an 18-month feeding study in mice were conducted to evaluate the potential chronic toxicity and oncogenicity of NMP in Crl:CD (SD)BR rats and B6C3F1/CrlBR mice. Groups of 62 male and female rats were administered diets containing 0, 1600, 5000, or 15,000 ppm of NMP for approximately 2 years. Groups of 50 male and female mice were administered diets containing 0, 600, 1200, or 7200 ppm NMP for approximately 18 months. In vivo parameters were evaluated weekly during the first 3 months of the study, and every other week or monthly during the remainder of the study. For rats, an ophthalmoscopic examination was conducted prior to study start and near the end of the study. Periodically, blood samples were collected from rats and mice for determination of leukocyte differential counts, and from mice for red blood cell morphology. After approximately 2 years of dietary administration in rats and 18 months in mice, all surviving animals were sacrificed. Selected tissues were processed for morphological evaluation. Over the course of the two-year study in rats, test substance-related decrements in body weight and weight gain occurred in 15,000 ppm males and females, which correlated with decreased food consumption and food efficiency. A toxicologically significant, test substance-related increase in the incidence of severe chronic progressive nephropathy occurred in 15,000 ppm males. Several morphological changes noted grossly and/or microscopically were secondary to the increased severity of chronic progressive nephropathy. NMP was not oncogenic in male or female rats at dietary concentrations of 15,000 ppm and below. A test substance-related decrease in the percentage of 15,000 ppm males surviving to the end of the two-year study compared to the control group resulted from the higher incidence of severe chronic progressive nephropathy. However, a sufficient population of 15,000 ppm rats were at risk for potential oncogenicity, so the lower survival did not impair the ability to detect an oncogenic response in this study. There were no adverse, test substance-related effects on the incidences of clinical observations, ophthalmic observations, or differential leukocyte counts in males or females, or on survival of females at any dietary concentration. Male and female mice administered dietary concentrations of 7200 ppm had significantly increased liver weight, significantly increased incidence of hepatocellular adenoma, and significantly increased foci of cellular alteration in the liver. At 7200 ppm, male mice also had an increased incidence of hepatocellular carcinoma while the increased incidence of hepatocellular carcinoma in female mice fell within the historical control range. In addition, the incidence of hepatocellular hypertrophy was increased in 7200 ppm males. Liver weight and hepatocellular hypertrophy were also increased in 1200 ppm males. There were no adverse, test substance-related effects on the incidences of clinical observations, food consumption, body weight, differential leukocyte counts, red blood cell morphology, or survival in either males or females at any dietary concentration. Under the conditions of the study, the no-observed-effect level for NMP was 5000 ppm for male and female rats, 600 ppm for male mice, and 1200 ppm for female mice.

Repeated exposure inhalation study of pentane in rats.

Pentane (CAS No. 109-66-0) is a chemical being used as a co-solvent in a polymer production facility with potential for inhalation exposure in humans. To assess the toxicity of pentane, groups of 10 male rats each were exposed by inhalation, 6 hr/day, 5 days/week for 2 weeks to either 0 (control), 1,000, 3,000 or 10,000 ppm. Five rats per group were killed following the 10th exposure; the remaining 5/group were killed after a 14-day post-exposure recovery period. Parameters investigated were clinical signs of toxicity, functional behavior, body weights, clinical pathology, and gross and microscopic pathology including organ weights. No unusual clinical observations were seen in the pentane-treated rats, and body weights were not altered. Test rats generally exhibited normal behavioral responses in the functional observational battery. Increases in serum calcium and phosphorus concentrations were seen in rats exposed to either 3,000 or 10,000 ppm. These were reversible during the 2-week recovery period. No other clinical pathology changes were observed and no pentane-related tissue pathology was seen in any of the groups. The no-observed-adverse-effect level was 1,000 ppm with reversible clinical pathology changes produced at 3,000 and 10,000 ppm.

Subchronic toxicity of cyclohexane in rats and mice by inhalation exposure.

Inhalation studies were conducted to determine the potential toxicity and/or potential neurotoxicity of cyclohexane. Groups of rats and mice were exposed to 0, 500, 2000, or 7000 ppm concentrations of cyclohexane vapor 6 hr/day, 5 days/week for 14 weeks. Subgroups of rats and mice were further observed during a 1-month recovery period. Functional observational battery (FOB) and motor activity (MA) behavioral tests were conducted on rats. These tests were conducted prior to the exposure series and during weeks 4, 8, and 13 on non-exposure days. Clinical pathology evaluations were conducted after approximately 7, 13, and 18 weeks. Approximately 14 and 18 weeks after study initiation, tissues from rats and mice were histologically processed and evaluated by light microscopy. During exposure to 2000 or 7000 ppm, rats and mice had a diminished response or an absent response to delivery of a punctate auditory alerting stimulus. Immediately following removal of rats from the inhalation chambers, 7000 ppm males and females and 2000 ppm females displayed a compound-related increase in the incidence of wet and/or stained fur (which occurred in the areas of the mouth, chin, and/or perineum). These signs were transient, were not observed during exposure or prior to exposure the following day, and were not associated with any behavioral or morphological changes. During exposure sessions, mice exposed to 7000 ppm exhibited clinical signs of toxicity which included hyperactivity, circling, jumping/hopping, excessive grooming, kicking of rear legs, standing on front legs, and occasional flipping behavior. Clinical signs of toxicity observed in 7000 ppm mice immediately after exposure included hyperactivity, hyperreactivity, ruffled fur (females only), gait abnormalities, spasms in both rear legs, and excessive grooming (males only). The clinical signs observed in mice during and immediately after exposure were transient, and were not present prior to the subsequent exposure. A few mice exposed to 2000 ppm appeared hyperactive during exposure in the latter portion of the study. There were no compound-related changes in mean body weights, body weight gains, food consumption, food efficiency, or mortality; and there were no ophthalmological abnormalities in rats or mice. In addition, there were no compound-related effects on 37 different behavioral parameters assessed during the FOB or during motor activity tests in rats. Male and female mice exposed to 7000 ppm had slight increases in measures of circulating erythrocyte mass (red blood cells, hemoglobin, hematocrit) and plasma protein concentration (males only). Male rats and male and female mice exposed to 7000 ppm had significantly increased relative liver weights, and 7000 ppm male mice also had significantly increased absolute liver weights at the end of the exposure period. At the end of the 1-month recovery period, absolute and relative liver weights of male and female mice were similar to control. However, relative liver weights of 7000 ppm male rats continued to be significantly higher at the end of the recovery period. Male and female rats exposed to 7000 ppm had a significantly increased incidence of hepatic centrilobular hypertrophy at the end of the exposure period, which was not observed at the conclusion of the 1-month recovery period. No microscopic changes were observed in mice. In rats, the no-observed-effect level (NOEL) for acute, transient effects was 500 ppm based on a diminished/absent response to an auditory alerting stimulus at 2000 ppm and above. The NOEL for subchronic toxicity in rats was 7000 ppm based on the lack of adverse effects on body weight, clinical chemistry, tissue morphology, and neurobehavioral parameters. In mice, the NOEL for acute, transient effects was 500 ppm based on behavioral changes during exposure at 2000 ppm and above. The NOEL for subchronic toxicity in mice is 2000 ppm based on hematological changes at 7000 ppm.

Toxicity of tetrafluoroethylene and S-(1,1,2, 2-tetrafluoroethyl)-L-cysteine in rats and mice.

Groups of 25 female F344 rats and 25 female B6C3F1 mice were exposed to 0, 30, 300, 600, or 1200 ppm tetrafluoroethylene (TFE) by inhalation for up to 12 days. Another set of 25 female rats and 25 female mice of the same strains were given 0, 5, 20, or 50 mg/kg of S-(1,1,2,2-tetrafluoroethyl)-L-cysteine (TFE-CYS) by oral gavage for 12 days. Both 12-day exposure regimens consisted of exposures for 5 consecutive days, a weekend with no exposures, and 4 consecutive daily exposures following the weekend. Five animals per group were sacrificed after the first exposure, the fifth exposure, and the ninth exposure for evaluation of cell proliferation in the liver and kidney. The remaining animals in each group (up to 10) were sacrificed after the ninth exposure (test day 12) for pathological evaluation of the liver, kidney, and spleen. Clinical pathology evaluations were performed on test day 11 or 12. Inhalation of TFE by rats and mice caused slight microscopic changes in the kidneys of rats and mice, but no histopathological changes in the liver. In the kidney, administration of TFE-CYS by gavage caused severe microscopic changes in rats, moderate-to-severe changes in mice, and no microscopic changes in the liver. Cell proliferation was increased in the kidneys of rats and mice given TFE by inhalation and TFE-CYS by gavage. TFE-CYS also caused increased liver weights and cell proliferation in the liver of rats and mice at the high doses. The cell proliferation response in the kidney and liver was transient in both species, being most pronounced after 5 days of exposure, and less evident or absent after 12 days of exposure. In the kidney, the cell proliferation and histopathologic response in rats was generally more pronounced than in mice. Kidney damage and cell proliferation were confined to the pars recta (P3) of the outer stripe of the outer medulla and medullary rays. Tubules in mice exposed to TFE and TFE-CYS had mostly regenerating cells by test day 12, while in rats the tubules still showed marked degeneration along with regeneration by the end of the study. The cortical labyrinth (P1 and P2 segments) was also affected at the 50 mg/kg dose of TFE-CYS in rats. Rats exposed to 50 mg/kg TFE-CYS had a mild anemia, and rats exposed to 1200 ppm TFE had slight, biologically inconsequential decreases in erythrocyte mass that may have been compound-related. In spite of the rather pronounced histopathologic changes in the kidneys of rats exposed to TFE-CYS, there was no clinical chemistry evidence for decreased kidney function. Increased levels of urinary fluoride were present in rats exposed to 300 ppm and greater of TFE, and in rats exposed to 20 and 50 mg/kg TFE-CYS. The spleen was not affected in this study. Overall, the results of this study suggest that effects of TFE could be attributed to the toxicity of TFE-CYS over the course of a 2-week exposure, as all effects that were seen with TFE were also seen with TFE-CYS.

Inhalation toxicity of cyclododecatriene in rats.

Cyclododecatriene (CDDT, CAS No. 4904-61-4) was tested for its inhalation toxicity in rats following repeated exposures. Male rats were exposed nose-only to CDDT for 6 hr/day, 5 days/wk for a total of 9 exposures over 2 weeks. Particular attention was paid to neurotoxicologic endpoints. Concentrations of 0 (control), 5, 50, and 260 ppm were studied. The 260 ppm chamber contained both vapor and aerosol while the 5 and 50 ppm chambers were vapor only. Four groups of 10 rats each were used to measure standard clinical signs and growth, clinical pathology (including hematology, biochemistries, and urine analysis), and tissue pathology. Another 4 groups of similar size were used for neurotoxicity testing. In the standard toxicity groups, 1/2 of the rats were sacrificed 1 day following the 9th exposure; the other half underwent a 2-week recovery period prior to being sacrificed (recovery group). During the exposures rats inhaling 260 ppm had a diminished or absent response to an alerting stimulus. Irregular respiration and lethargy were observed in these rats immediately following exposure. These signs were rapidly reversible and were not seen prior to the subsequent exposure. Body weights in rats exposed to either 50 or 260 ppm were significantly lower than the corresponding controls. No compound-related clinical pathology changes were seen in any of the test groups and tissue pathology effects only occurred in the nasal tissue. In rats exposed to 260 ppm, minimal degeneration/necrosis of nasal olfactory epithelium was observed in rats examined immediately following the exposure period. This change was not seen in the recovery rats. Functional observational battery (FOB) assessments and motor activity (MA) evaluations conducted after the 4th and 9th exposures on rats from all test groups, and specific neuropathologic evaluation on perfused brain, spinal cord, and skeletal muscle from rats exposed to 260 ppm failed to demonstrate any specific neurotoxicity. Outward signs of sedation were seen at the top level tested. Under the conditions of this test, the no-observed-adverse-effect level (NOAEL) was determined to be 5 ppm based upon a reduced rate of body weight gain in the 50 ppm group. No specific neurotoxicity was detected and the histopathologic response was limited to reversible changes in the nasal epithelia in rats exposed to 260 ppm.

90-day subchronic toxicity study in rats and mice fed N-methylpyrrolidone (NMP) including neurotoxicity evaluation in rats.

In mice, there were no effects on body weight or food consumption. As observed in rats, mice fed 2,500 or 7,500 ppm exhibited a change in urine coloration which was not associated with morphological changes in cholesterol, triglycerides, calcium, and alkaline phosphatase occurred at 28 days but not 90 days. These changes are thus assessed as being of minor toxicological relevance. Liver weights were elevated in males fed 2,500 or 7,500 ppm and centrilobular hypertrophy was seen in both sexes fed 7,500 ppm. These changes may be regarded as an adaptation process but are clearly related to NMP exposure. Other toxicological endpoints examined were unaffected by NMP. The NOAEL was 3,000 ppm for both sexes of rats based on body weight effects and changes in 3 neurobehavioral parameters (males only) at higher feeding levels. In mice, the NOAEL was 1,000 ppm based on liver responses to higher concentrations.

T-cell co-stimulation through B7RP-1 and ICOS.

T-cell activation requires co-stimulation through receptors such as CD28 and antigen-specific signalling through the T-cell antigen receptor. Here we describe a new murine costimulatory receptor-ligand pair. The receptor, which is related to CD28 and is the homologue of the human protein ICOS, is expressed on activated T cells and resting memory T cells. The ligand, which has homology to B7 molecules and is called B7-related protein-1 (B7RP-1), is expressed on B cells and macrophages. ICOS and B7RP-I do not interact with proteins in the CD28-B7 pathway, and B7RP-1 co-stimulates T cells in vitro independently of CD28. Transgenic mice expressing a B7RP-1-Fc fusion protein show lymphoid hyperplasia in the spleen, lymph nodes and Peyer's patches. Presensitized mice treated with B7RP-1-Fc during antigen challenge show enhanced hypersensitivity. Therefore, B7RP-1 exhibits co-stimulatory activities in vitro and in vivo. ICOS and B7RP-1 define a new and distinct receptor-ligand pair that is structurally related to CD28-B7 and is involved in the adaptive immune response.

Chronic toxicity, oncogenicity, and mutagenicity studies with chlorotetrafluoroethane (HCFC-124).

The chronic toxicity, oncogenicity, and mutagenicity of chlorotetrafluoroethane (HCFC-124) were evaluated. In the chronic toxicity/oncogenicity study, male and female rats were exposed to 0, 2000, 10,000, or 50,000 ppm HCFC-124 for 6 hr/day, 5 days/week, for 2 years. Body weights were obtained weekly during the first three months of the study and every other week for the remainder of the study. Food consumption was determined weekly. Clinical signs of toxicity were monitored throughout the study. An ophthalmological examination was performed on all animals prior to study start, and all surviving rats were examined at approximately 3, 12, and 24 months after study start. Clinical pathology was evaluated at 3, 6, 12, 18, and 24 months. An interim termination was conducted at 12 months. All surviving rats were necropsied at 24 months. A complete set of tissues was collected for microscopic examination, and selected tissues were weighed. There were no compound-related, adverse effects on body weight, food consumption, survival, clinical signs of toxicity, ophthalmoscopically observable ocular lesions, serum hormone concentrations, or clinical pathology parameters at any exposure concentration in either male or female rats. Compared to controls, urine fluoride was increased in males and females at all exposure concentrations, and plasma fluoride was increased in females at all exposure concentrations. Excretion of fluoride represents conversion of the parent molecule, and as such is not considered to be an adverse effect. There were no toxicologically significant, compound-related organ weight changes or gross or microscopic findings in male or female rats at any of the exposure concentrations tested. HCFC-124 was not toxic or carcinogenic in rats of either sex after inhalation exposure at concentrations of up to 50,000 ppm in this two-year chronic toxicity/oncogenicity study. After exposure to HCFC-124 for six hours per day, five days per week, for 24 months, the no-observed-adverse-effect level for male and female rats was 50,000 ppm. HCFC-124 was not mutagenic in Salmonella typhimurium strains TA1535, TA97, TA98, and TA100 with and without activation when evaluated at concentrations up to 60% HCFC-124 for 48 hours. No evidence of clastogenic activity was observed in cultured human lymphocytes at atmospheric concentrations up to 100% HCFC-124 for 3 hours, with and without metabolic activation. In vivo, no micronuclei were induced in mouse bone marrow cells following exposure of mice to concentrations of 99,000 ppm HCFC-124 6 hours/day for 2 days.

90-day feeding and one-generation reproduction study in Crl:CD BR rats with 17 beta-estradiol.

Over the past several years, there has been increasing concern that chemicals and pesticides found in the environment may mimic endogenous estrogens, potentially producing adverse effects in wildlife and human populations. Because estrogenicity is one of the primary concerns, a 90-day/one-generation reproduction study with 17 beta-estradiol was designed to set dose levels for future multigenerational reproduction and combined chronic toxicity/oncogenicity studies. The purpose of these studies is to evaluate the significance of a range of responses as well as to provide benchmark data for a risk assessment for chemicals with estrogen-like activities. This 90-day/one-generation reproduction study was conducted in male and female Crl:CD BR rats using dietary concentrations of 0, 0.05, 2.5, 10, and 50 ppm 17 beta-estradiol. Endpoints were chosen in order to evaluate both subchronic and reproductive toxicity. In addition, several mechanistic/biochemical endpoints were evaluated for their usefulness in follow-up studies. In the P1 generation, dietary administration of 2.5, 10, and 50 ppm 17 beta-estradiol produced dose-dependent decreases in body weight, body weight gain, food consumption, and food efficiency. At 10 and 50 ppm 17 beta-estradiol, minimal to mild nonregenerative anemia, lymphopenia, decreased serum cholesterol (50 ppm only), and altered splenic lymphocyte subtypes were also observed in the P1 generation. Additionally, at these concentrations, there were changes in the weights of several organs. Evidence of ovarian malfunction, characterized by reduced numbers of corpora lutea and large antral follicles, was observed at 2.5 ppm 17 beta-estradiol and above. Other pathologic changes in males and females fed 10 and 50 ppm 17 beta-estradiol included centrilobular hepatocellular hypertrophy; diffuse hyperplasia of the pituitary gland; feminization of the male mammary glands; mammary gland hyperplasia in females; increased number of cystic follicles in the ovary; hypertrophy of the endometrium and endometrial glands in the uterus; degeneration of seminiferous epithelium; and atrophy of the testes and the accessory sex glands. In the reproduction portion of this study, rats fed 10 or 50 ppm 17 beta-estradiol did not produce litters. While there was no evidence that the 50 ppm treated rats mated, 33.3% of the rats fed 10 ppm mated but did not produce litters. No effects on mating and fertility indices were observed in rats fed 0.05 and 2.5 ppm 17 beta-estradiol. Pup weights at birth were statistically decreased relative to control in the groups fed 0.05 and 2.5 ppm 17 beta-estradiol. Weights of the rats in the 0.05 ppm group recovered by postnatal day 4 and remained similar to control throughout the remainder of the study. The mean gestation length of the 0.05 ppm group was slightly, albeit not statistically significantly, shorter (0.5 days) than that of the control group, which may have contributed to the decrease in birth weight of the 0.05 ppm group. In contrast, the weights of the F1 generation rats fed 2.5 ppm 17 beta-estradiol remained decreased relative to the control group throughout the study. Parental administration of 17 beta-estradiol did not alter anogenital distance in male or female pups. The onset of sexual maturation, as measured by day of preputial separation in males and day of vaginal opening in females, was delayed in male rats fed 2.5 ppm (by 8.2 days) and was hastened in female rats fed 0.05 and 2.5 ppm (by 1.6 and 8.8 days, respectively). The age at vaginal opening ranged from 26 to 37, 26 to 35, and 21 to 25 days for rats fed 0, 0.05, and 2.5 ppm 17 beta-estradiol, respectively. Hence, the range of age at vaginal opening was similar between the control and 0.05 ppm group. The organ weight and pathologic alterations observed in the adult F1 generation rats were similar to those observed in the P1 generation rats. (ABSTRACT TRUNCATED)

A Neu differentiation factor (NDF) domain essential for proliferation and alterations in morphology of colonic epithelial cells in vitro.

The Neu Differentiation Factors (NDFs, also termed "heregulins") are a family of proteins that were first isolated as ligands for the HER2 (ergB2, or p185neu) receptor protein tyrosine kinase. Here we show that NDF acts to stimulate the proliferation and alter the cellular morphology of colonic epithelial cells in culture. Dramatic NDF-induced changes in cellular morphology were noted in the colonic epithelial cell line, LIM 1215. In addition, the expression of specific cell proteins, such as carcinoembryonic antigen and integrin beta 4, was induced in LIM 1215 cells by NDF. These effects were more pronounced with the beta isoform than with the alpha isoform of NDF. The EGF-homology domain of NDF beta was sufficient to stimulate the proliferation and alteration in cell morphology. The use of chemically synthesized chimeric NDF alpha and NDF beta proteins enabled use to identify a region of seven amino acids in the EGF-homology domain of NDF beta that is required for both activities. These in vitro experiments suggest that NDF may act as a regulator of growth and differentiation of colonic epithelial cells in vivo.

Further evaluation of the incorporation of an immunotoxicological functional assay for assessing humoral immunity for hazard identification purposes in rats in a standard toxicology study.

A previous study (Ladics et al., 1995) conducted in our laboratory using the known immunosuppressant agent, cyclophosphamide, indicated that a functional assay for assessment of humoral immunity may be conducted in rats in a standard toxicology study. The objective of this study was to further examine the feasibility of conducting an immunotoxicological assay for assessing humoral immunity in rats in a standard toxicology study using a chemical, carbon tetrachloride (CCl4), whose principal target organ of toxicity is not the immune system. Specifically, the previous study and this study were done to determine whether the conduct of an assay for assessing humoral immune function would affect standard toxicological endpoints. Male CD rats were untreated or dosed orally for 30 or 90 days, excluding weekends, with vehicle or 12.5 or 25 mg/kg CCl4. Six days prior to sacrifice, selected rats were injected intravenously with sheep red blood cells (SRBC) for assessment of humoral immune function. One day prior to necropsy, blood for hematological and clinical chemical measurements was collected from each rat. On the day of necropsy standard protocol tissues were collected, weighed, processed to slides, and later examined microscopically. One-half of each spleen was used to assess spleen cell numbers and quantitate lymphocyte subsets (Thelper; Tcyt/sup; total T- and B-cells) by flow cytometry. Serum was analyzed for anti-SRBC IgM antibody by using an enzyme-linked immunosorbent assay. Administration of 12.5 and 25 mg/kg CCl4 for 30 days decreased SRBC-specific serum IgM levels 42 and 45%, respectively, while 25 mg/kg CCl4 for 90 days increased SRBC-specific IgM levels by 50%. CCl4 did not alter splenic lymphocyte subset numbers nor the weight nor morphology of lymphoid organs. Exposure to 25 mg/kg CCl4 did increase liver weight and serum sorbitol dehydrogenase levels, as well as produce centrilobular fatty change. SRBC administration did not alter any hematological or clinical chemistry parameters, nor lymphocyte subset numbers. With the expected exception of the spleen (slight increase in number and size of germinal centers), administration of SRBC did not significantly alter the weights or morphology of routine protocol tissues. Furthermore, administration of SRBC did not mask the rather mild hepatotoxic effects of CCL4 exposure observed in this study. Based on these and previous findings, it appears that a functional assay for assessing humoral immunity may be conducted in animals on standard toxicology study without altering standard toxicological endpoints.

Mechanisms for the pancreatic oncogenic effects of the peroxisome proliferator Wyeth-14,643.

Several peroxisome proliferators have been shown to produce pancreatic acinar cell hyperplasia/adenocarcinomas in 2-year bioassays with rats: ammonium perfluorooctanoate (C8), clofibrate, methylclofenapate, HCFC-123, and Wyeth-14,643 (WY). We have used in vitro (C8, WY) and in vivo (WY) approaches to examine several possible mechanisms of pancreatic tumorigenesis by peroxisome proliferating compounds. These mechanisms include cholecystokinin receptor agonism (CCK(A)), trypsin inhibition, alterations in gut fat content, cholestasis, and altered bile flow/composition. All of these mechanisms enhance pancreatic growth either by binding to the CCK(A) receptor or by increasing plasma CCK levels. In vitro experiments using a receptor competition binding assay demonstrated that WY and C8 do not bind directly to the CCK(A) receptor. In a continuous spectrophotometric assay, WY and C8 also failed to inhibit trypsin, a common mechanism for increasing plasma CCK levels. These in vitro results suggested that WY was not acting via the two most common mechanisms for modulation of pancreas growth. Two types of in vivo experiments were conducted. The subchronic study (2-month duration) was designed primarily to detect early changes in pancreatic growth such as those mediated by compounds that inhibit trypsin or act as CCK(A) receptor agonists. The chronic study (6 months) was designed primarily to evaluate whether the pancreatic lesions were secondary to hepatic changes such as cholestasis and/or altered bile flow/composition. In the in vivo experiments, male Crl:CDBR rats were fed diets containing 0 or 100 ppm WY. In the subchronic study WY-treated rats had a twofold increase in mean relative liver weights, an eightfold increase in hepatic peroxisomal proliferation, and a fourfold increase in hepatocyte cell proliferation after 1 week which remained elevated throughout the 2 months of treatment. In contrast, no pancreatic weight effects, increases in plasma CCK, or acinar cell proliferation was seen through 2 months in the WY group when compared to the control group. Fecal fat concentrations were also measured at 2 months and demonstrated no difference between control and WY-treated animals. The absence of any early pancreas changes in the subchronic study is consistent with the in vitro data which demonstrated that WY is not a CCK(A) agonist or a trypsin inhibitor. The chronic study demonstrated increases in pancreatic weights at 3 months (6% above control) and 6 months (17% above control), as well as increased CCK plasma levels in the WY-treated group. Liver effects in the chronic study paralleled those of the subchronic time points. Clinical pathology endpoints including increased serum concentrations of bile acids, alkaline phosphatase, and bilirubin were indicative of cholestasis in the chronic WY-treated group. The cholestasis may be responsible for the downward trend in total bile acid output, both of which may contribute to the modest increases in plasma CCK levels. These results indicate that chronic exposure to WY causes liver alterations such as cholestasis, which may increase plasma concentrations of CCK. Hence, WY may induce pancreatic acinar cell adenomas/adenocarcinomas via a mild but sustained increase in CCK levels secondary to hepatic cholestasis.

Induction of coagulation effects by Wyeth-14,643 in Crl:CD BR rats.

A two-year mechanistic bioassay in male Crl:CD BR rats was initiated with 50 ppm Wyeth-14,643 (WY) to investigate the relationship between peroxisome proliferating compounds and Leydig cell adenoma formation. After 154 days, the survival rate in the WY group decreased below control levels. After 300 days, the dose was lowered to 25 ppm for the remainder of the study. Gross examination of WY-treated rats either found dead or euthanized in extremis revealed hemorrhages at several sites. To investigate this observation, blood was then collected on test day 281 from 10 randomly selected control and WY-treated rats and a clinical pathological examination was performed. The WY-treated rats had significantly decreased red blood cell count, hemoglobin, and hematocrit, and elevated platelet counts. In the WY-treated rats, prothrombin times in undiluted plasma were similar to the controls, but were markedly prolonged in 2 of 10 rats when the plasma samples were diluted to 25%. Subsequently, blood was collected prior to sacrificing WY-treated rats which were exhibiting clinical signs of anemia. These rats had prolonged prothrombin times, activated partial thromboplastin time, and thrombin clot time when compared to laboratory historical control data (116.7 vs 13.3, 116.4 vs 13.7, and 42.4 vs 25.7 seconds, respectively). In a subsequent, ongoing study, Vitamin K was added to control and WY-treated diets (100 ppm). No survival differences between control and WY-treated rats occurred through 260 days in this second study. These new data suggest that deaths in the WY-treated group in our initial study were due to a vitamin K deficiency. The role of increased serum estradiol, its effects on blood coagulation, and enhanced hepatic cell proliferation in the vitamin K-dependent coagulation processes warrant further investigation.

Repeated dose toxicity study (28 days) in rats and mice with N-methylpyrrolidone (NMP).

Twenty-eight day feeding studies were conducted to evaluate the repeated dose toxicity of NMP, a widely used industrial solvent, in Crl:CD BR rats and B6C3F1 mice. Groups of 5 male and 5 female rats each were fed either 0, 2,000, 6,000, 18,000, or 30,000 ppm NMP; similar groups of mice were fed either 0, 500, 2,500, 7,500, or 10,000 ppm. In vivo parameters, hematology and clinical chemistry parameters, and complete pathology evaluations were conducted after approximately 28 days. Decrements in mean body weight gains, reflecting decreases in food consumption and efficiency, were seen in male rats fed 18,000 ppm and in both sexes fed 30,000 ppm. In rats, clinical chemical changes, indicating possible compound-related alterations in lipid, protein, and carbohydrate metabolism, occurred at 18,000 ppm in males and 30,000 ppm in both sexes. No histopathological changes in rats were judged to be directly related to NMP exposure. Hematological (mild to moderate leukopenia) and histopathological alterations (hypocellular bone marrow, testicular degeneration and atrophy, and thymic atrophy) were judged to be secondary to nutritional and body weight effects in male and/or female rats at 30,000 ppm. In mice, cloudy swelling of the epithelia of the distal parts of the renal tubuli was observed in 4 males and 3 females at 10,000 ppm and in 2 male mice at 7,500 ppm. For both rats and mice, abnormal urine coloration was observed (in mice at 2,500 ppm and above, and in rats at 18,000 ppm and above). The discoloration was interpreted as a sign of systemic availability of the test substance, but not as an adverse effect. The NOAEL was 6,000 ppm for male rats and 18,000 ppm for female rats. In mice, the NOAEL was 2,500 ppm based on the kidney histopathology.

Differential subcellular localization, expression and biological toxicity of BRCA1 and the splice variant BRCA1-delta11b.

The mechanism of BRCA1 tumor suppression in human breast and ovarian cells is the focus of intense investigation. In this report, full length BRCA1 (230 kDa) introduced into cells with CMV promoter constructs was nuclear when transgene expression was low whereas high expression resulted in cytoplasmic accumulation, aberrant nuclear and cell morphology. A nuclear localization signal (NLS) was mapped to BRCA1 amino acid positions 262-570. We describe a splice variant, BRCA1-delta11b, missing the majority of exon 11 including the NLS. Exogenous BRCA1-delta11b (110 kDa) was cytoplasmic and, unlike the full-length protein, overexpression of the protein encoded by the variant did not appear to be toxic. RNA probe titrations and RT-PCR demonstrated that BRCA1 and delta11b transcripts are coexpressed in a wide variety of cells and tissues. Interestingly, BRCA1-delta11b message was greatly reduced or absent in several breast and ovarian tumor lines relative to exon 11 transcripts and a delta9,10 splice variant. Taken together our results suggest that full-length BRCA1 and BRCA1-delta11b may have distinct roles in cell growth regulation and tumorigenesis.

Subchronic toxicity of 4-vinylcyclohexene in rats and mice by inhalation exposure.

This study was conducted to evaluate the subchronic toxicity of 4-vinylcyclohexene (VCH). Male and female Sprague-Dawley rats and B6C3F1 mice were exposed by inhalation to VCH 6 hr/day, 5 days/week for 13 weeks. Rats were exposed to 0, 250, 1000, or 1500 ppm, and mice were exposed to 0, 50, 250, or 1000 ppm. In addition, another group of rats and mice was exposed to 1000 ppm butadiene so that a comparison could be made between the two compounds. Exposure to 1000 ppm VCH resulted in deaths of all male mice and 5/10 female mice on Test Days 11 or 12. Three additional female mice exposed to 1000 ppm VCH died prior to study completion. The most notable compound-related clinical sign was lethargy observed in the 1500 ppm VCH-exposed rats and 1000 ppm VCH-exposed mice. Male rats exposed to 1500 ppm VCH had significantly lower body weights compared to controls, and male and female rats in the 1500 ppm group had significantly lower body weight gains. None of the VCH-exposed animals or butadiene-exposed rats showed any compound-related hematological effects. However, mice exposed to 1000 ppm butadiene exhibited mild macrocytic anemia. Clinical chemistry evaluation and urinalysis showed no compound-related effects in rats exposed to either VCH or butadiene. Male and female rats exposed to 1000 or 1500 ppm VCH or 1000 ppm butadiene had increased absolute and/or relative liver weights, and male rats in these same exposure groups had increased relative kidney weights. Microscopically, increased accumulation of hyaline droplets was observed in the kidneys of male rats from all VCH exposure groups. Although compound-related, the droplets were not accompanied by cytotoxicity. In mice, the most notable adverse histopathological effect was ovarian atrophy in females exposed to 1000 ppm VCH or 1000 ppm butadiene. The atrophy was slightly more severe in the VCH-exposed females than in the butadiene-exposed females. There were no other compound-related pathological effects in male or female mice exposed to VCH. Additionally, butadiene-exposed male mice had decreased testicular weights, accompanied by slight testicular degeneration and atrophy. For VCH exposure, the no-observed-adverse-effect-level is 1000 ppm for rats based on lethargy and lowered body weights and 250 ppm for mice based on mortality and ovarian atrophy.

Subchronic toxicity and teratogenicity of 2-chloro-1,1,1,2-tetrafluoroethane (HCFC-124).

Inhalation studies were conducted to determine the potential toxicity of HCFC-124. Groups of rats and mice were exposed to HCFC-124 6 hr/day, 5 days/week for 13 weeks at 0, 5000, 15,000, and 50,000 ppm. Subgroups of rats and mice were held for a 1-month recovery period. A functional observational battery (FOB) was conducted on rats at 0, 4, 13, and 16 weeks. Clinical pathology evaluations were conducted at 7, 13, and 17 weeks. Thirteen or 17 weeks after study initiation, rats and mice underwent gross and microscopic evaluation, and livers were evaluated for hepatic beta-oxidation activity. In addition, groups of female rats and rabbits were exposed to HCFC-124 by inhalation during gestation to 0, 5000, 15,000, or 50,000 ppm. Exposure of rats and mice to HCFC-124 caused minimal compound-related effects. Compound-related changes occurred in several clinical pathology parameters in rats and mice. Hepatic beta-oxidation activity was significantly higher in 5000, 15,000, and 50,000 ppm male mice; however, there were no compound-related effects on beta-oxidation activity in rats. During the daily exposures, rats, mice, and rabbits exposed to 50,000 ppm were less responsive to auditory stimuli or less active compared to controls. At the 13-week FOB, male rats exposed to 15,000 or 50,000 ppm had decreased arousal. There were no compound-related effects on mortality, clinical signs, ocular tissues, hematology parameters, organ weights, and tissue morphology at any concentration in rats or mice. Maternal toxicity in rats was evident by a significant decrease in weight gain and food consumption at 50,000 ppm. Similarly, 50,000 ppm pregnant rabbits had lower food consumption. However, for both rats and rabbits, there was no evidence of fetal toxicity at any concentration.

Chronic toxicity/oncogenicity of dimethylacetamide in rats and mice following inhalation exposure.

The potential chronic toxicity and oncogenicity of dimethylacetamide (DMAC) was evaluated by exposing male and female rats and mice to 0, 25, 100, or 350 ppm DMAC for 6 hr/day, 5 days/week for 18 months (mice) or 2 years (rats). Clinical pathology was evaluated at 3, 6, 12, 18, and 24 (rats only) months. An interim euthanization for rats occurred at 12 months and hepatic cell proliferation in rats and mice was examined at 2 weeks and 3 and 12 months. No compound-related effects on survival were observed. Rats exposed to 350 ppm had lower body weight and/or body weight gain. There were no compound-related effects on body weight or weight gain in mice at any concentration. There were no compound-related adverse effects on the incidence of clinical signs of toxicity in rats or mice. No hematologic changes were observed in either species. Serum sorbitol dehydrogenase activity was increased in rats exposed to 350 ppm. Serum cholesterol and glucose concentrations were significantly higher in 100 and 350 ppm female rats. Compound-related morphological changes were observed in the liver. In rats, exposure to 100 or 350 ppm produced increased absolute and/or relative liver weights, hepatic focal cystic degeneration, hepatic peliosis, biliary hyperplasia (350 ppm only), and lipofuscin/hemosiderin accumulation in Kupffer cells. In mice, exposure to 100 or 350 ppm produced increased absolute and relative liver weights (350 ppm females only), accumulation lipofuscin/hemosiderin in Kupffer cells, and centrilobular single cell necrosis. Male rats exposed to 350 ppm also had significantly higher absolute and relative kidney weights which correlated with the gross and microscopic changes resulting from a compound-related increase in severity of chronic progressive nephropathy. Female mice exposed to 350 ppm had an increased incidence of bilateral, diffuse retinal atrophy. No increase in hepatic cell proliferation was seen in mice or rats at any exposure concentration. DMAC was not oncogenic under these experimental conditions in either the rat or mouse. The NOAEL for male and female rats and mice is 25 ppm.