Gene/Protein Disease Symptom Drug Enzyme Compound
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Query: UMLS:C0019204 (hepatocellular carcinoma)
 71,386 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

2-Butoxyethanol is a member of a family of ethylene glycol monoalkyl ethers. It is used extensively as a solvent in surface coatings such as lacquers, enamels, varnishes, and latex paint; in paint thinners, paint stripping formulations, and inks; and in degreasers and industrial and household cleaners. 2-Butoxyethanol was nominated for study because of its widespread use in industrial and consumer applications, the potential for exposure to workers and the general population, and the absence of chronic toxicity data. Male and female F344/N rats and B6C3F1 mice were exposed to 2-butoxyethanol (greater than 99% pure) by inhalation (primary route of human exposure) for 14 weeks or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium, cultured Chinese hamster ovary cells, and the bone marrow of male F344/N rats and B6C3F1 mice. 14-WEEK STUDY IN RATS: Groups of 10 male and 10 female rats were exposed to 2-butoxyethanol by inhalation at concentrations of 0, 31, 62.5, 125, 250, or 500 ppm, 6 hours per day, 5 days per week for 14 weeks. One female rat in the 250 ppm group was killed moribund during week 8; four females in the 500 ppm group were killed moribund during week 1 and one during week 5. Final mean body weights of females exposed to 500 ppm were significantly less than those of the chamber controls. Clinical findings included abnormal breathing, pallor, red urine stains, nasal and eye discharge, lethargy, and increased salivation and/or lacrimation. Due to vascular thrombosis and infarction in the tail vertebrae of 500 ppm female rats, the tails became necrotic and either sloughed off or were chewed off. The primary effect on the hematopoietic system was an anemia characterized as macrocytic, normochromic, and regenerative in males exposed to 125 ppm or greater and, to a greater extent, in all exposed groups of females. Compared to the chamber controls, kidney weights of males exposed to 500 ppm and females exposed to 125 ppm or greater and liver weights of males exposed to 250 or 500 ppm and females exposed to 125 ppm or greater were significantly increased, and thymus weights of females exposed to 500 ppm were significantly less. In female rats killed moribund, there was considerable histologic evidence of thrombosis in tissues and organs including the nasal cavity, incisors, liver, lung, and heart. In addition to thrombosis, infarction occurred in the vertebrae of the tail resulting in necrosis and loss of the distal portion of the tail. There were also inflammation, necrosis, and ulceration of the forestomach; necrosis and centrilobular degeneration of the liver; renal tubule degeneration; and atrophy of the spleen and thymus. Exposure-related increases in the incidences of Kupffer cell pigmentation, forestomach inflammation and epithelial hyperplasia, bone marrow hyperplasia, splenic hematopoietic cell proliferation, and renal tubule pigmentation were observed in male and/or female rats surviving to the end of the study. 14-WEEK STUDY IN MICE: Groups of 10 male and 10 female mice were exposed to 2-butoxyethanol by inhalation at concentrations of 0, 31, 62.5, 125, 250, or 500 ppm, 6 hours per day, 5 days per week for 14 weeks. Two male and two female mice exposed to 500 ppm died and two males and two females were killed moribund during the first 2 weeks of the study. Final mean body weights of 125, 250, and 500 ppm male mice were significantly less than those of the chamber controls. Clinical findings were observed only in 500 ppm males and females that died or were killed moribund and included abnormal breathing, red urine stains, and lethargy. Hematologic evaluation indicated an anemia that was characterized as normocytic, normochromic, and regenerative in mice exposed to 62.5 ppm or greater; the anemia was more pronounced in females. Liver weights of males exposed to 500 ppm were significantly greater than the chamber controls. In mice either dying early or killed moribund, there were inflammation, necrosis, and ulceration of the forestomach; mediastinal pleura and peritoneal inflammationmmation associated with the forestomach lesions; liver necrosis; renal tubule degeneration; atrophy of the spleen, thymus, and mandibular and mesenteric lymph nodes; and degeneration of the testis. Exposure-related increases in the incidences of hematopoietic cell proliferation and hemosiderin pigmentation of the spleen, Kupffer cell hemosiderin pigmentation of the liver, inflammation and epithelial hyperplasia of the forestomach, and renal tubule hemosiderin pigmentation occurred in male and/or female mice surviving to the end of the study. 2-YEAR STUDY IN RATS: Groups of 50 male and 50 female rats were exposed to 2-butoxyethanol by inhalation at concentrations of 0, 31.2, 62.5, or 125 ppm, 6 hours per day, 5 days per week for 104 weeks. For hematology and bone marrow analyses, additional groups of 27 male and 27 female rats were exposed to 0, 62.5, or 125 ppm for evaluation at 3, 6, and 12 months and nine male and nine female rats were exposed to 31.2 ppm for evaluation at 3 (hematology only) and 6 months. Survival and Body Weights: Survival of exposed male and female rats was similar to the chamber control groups. The mean body weights of females exposed to 125 ppm were generally less than the chamber control group. Hematology and Bone Marrow Cellularity: The most consistent exposure-related effect on the hematopoietic system was an exposure concentration-related mild macrocytic, normochromic, regenerative anemia present at 3, 6, and 12 months, with females more affected than males. Significant increases in bone marrow cellularity and decreases in the myeloid/erythroid ratio relative to the chamber controls were observed at all time points in females exposed to 125 ppm, and a decrease in the myeloid/erythroid ratio was observed in males exposed to 125 ppm at 12 months. Pathology Findings: The incidence of benign or malignant pheochromocytoma (combined) of the adrenal medulla in females exposed to 125 ppm was not significantly increased compared to the chamber controls but exceeded the historical control range. Exposure-related increases in the incidences of hyaline degeneration of the olfactory epithelium and Kupffer cell pigmentation of the liver were observed in male and female rats. 2-YEAR STUDY IN MICE: Groups of 50 male and 50 female mice were exposed to 2-butoxyethanol by inhalation at concentrations of 0, 62.5, 125, or 250 ppm, 6 hours per day, 5 days per week for 104 weeks. For hematology and bone marrow analyses, additional groups of 30 male and 30 female mice were exposed to 0, 62.5, 125, or 250 ppm for evaluation at 3, 6, and 12 months. Survival and Body Weights: Survival of male mice exposed to 125 or 250 ppm was significantly less than that of the chamber control group. The mean body weights of exposed males were generally less than those of the chamber control group during the last 6 months of the study. The mean body weights of exposed female mice were less than those of the chamber control group; the reductions were greater and occurred earlier than those observed in males. Hematology: The most consistent exposure-related effect on the hematopoietic system was an exposure concentration-related minimal normocytic, normochromic, regenerative anemia present at 3, 6, and 12 months, with females affected slightly more than males. Pathology Findings: In females exposed to 250 ppm, incidences of forestomach squamous cell papilloma and squamous cell papilloma or carcinoma (combined) were significantly increased relative to the chamber controls, and these incidences exceeded the ranges in historical chamber controls. In 2-butoxyethanol exposed males, there were possible exposure-related increases in the incidences of squamous cell papilloma of the forestomach, although the increases were not significant and the incidences were within the historical control range for chamber controls. Accompanying these neoplasms in females and, to a lesser extent, in males were exposure-related increases in the incidences of ulcer and epithelial hyperplasia of the forestomach. In male mice exposed to 250 ppm, the incidence of hemangiosarcoma of the liver was significantly increased relative to chamber controls and exceeded the range in historical controls; in addition, there were possible exposure-related increases in the incidence of hepatocellular carcinoma. Incidences of hemosiderin pigmentation in the Kupffer cells were significantly increased in 125 and 250 ppm males and all exposed groups of females. The incidences of splenic hematopoietic cell proliferation and hemosiderin pigmentation were generally increased in males and females, and the incidences of bone marrow hyperplasia were increased in males. The incidences of hyaline degeneration of the olfactory and respiratory epithelia of the nose were increased in female mice. GENETIC TOXICOLOGY: 2-Butoxyethanol did not induce mutations in any of the S. typhimurium strains tested, with or without induced hamster or rat liver S9. 2-Butoxyethanol induced cycle delay but did not induce either sister chromatid exchanges or chromosomal aberrations in cultured Chinese hamster ovary cells with or without S9. 2-Butoxyethanol did not induce micronuclei in bone marrow cells of male rats or mice administered the chemical by intraperitoneal injection three times at 24-hour intervals. CONCLUSIONS: Under the conditions of these 2-year inhalation studies, there was no evidence of carcinogenic activity of 2-butoxyethanol in male F344/N rats exposed to 31.2, 62.5, or 125 ppm. There was equivocal evidence of carcinogenic activity of 2-butoxyethanol in female F344/N rats based on the increased combined incidences of benign or malignant pheochromocytoma (mainly benign) of the adrenal medulla. There was some evidence of carcinogenic activity of 2-butoxyethanol in male B6C3F1 mice based on increased incidences of hemangiosarcoma of the liver. A marginal increase in the incidences of forestomach squamous cell papilloma and an increase in the incidences of hepatocellular carcinoma may have been exposure related. There was some evidence of carcinogenic activity of 2-butoxyethanol in female B6C3F1 mice based on increased incidences of fore stomach squamous cell papilloma or carcinoma (mainly papilloma). Increased incidences of forestomach neoplasms in male and female mice occurred in groups in which ulceration and hyperplasia were also present. Exposure to 2-butoxyethanol caused a mild regenerative anemia and effects secondary to the anemia. Synonyms: 2-Butoxy-1-ethanol; m-butyl ether; butyl glycol; ethylene glycol monobutyl ether Trade name: Butyl Cellosolve
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PMID:NTP Toxicology and Carcinogenesis Studies 2-Butoxyethanol (CAS NO. 111-76-2) in F344/N Rats and B6C3F1 Mice (Inhalation Studies). 1257 79

DIOXIN TOXIC EQUIVALENCY FACTOR EVALUATION OVERVIEW: Polyhalogenated aromatic hydrocarbons such as 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) have the ability to bind to and activate the ligand-activated transcription factor, the aryl hydrocarbon receptor (AhR). Structurally related compounds that bind to the AhR and exhibit biological actions similar to TCDD are commonly referred to as "dioxin-like compounds" (DLCs). Ambient human exposure to DLCs occurs through the ingestion of foods containing residues of DLCs that bioconcentrate through the food chain. Due to their lipophilicity and persistence, once internalized they accumulate in body tissue, mainly adipose, resulting in chronic lifetime human exposure. Since human exposure to DLCs always occurs as a complex mixture, the toxic equivalency factor (TEF) methodology has been developed as a mathematical tool to assess the health risk posed by complex mixtures of these compounds. The TEF methodology is a relative potency scheme that ranks the dioxin-like activity of a compound relative to TCDD, which is the most potent congener. This allows for the estimation of the potential dioxin-like activity of a mixture of chemicals, based on a common mechanism of action involving an initial binding of DLCs to the AhR. The toxic equivalency of DLCs was nominated for evaluation because of the widespread human exposure to DLCs and the lack of data on the adequacy of the TEF methodology for predicting relative potency for cancer risk. To address this, the National Toxicology Program conducted a series of 2-year bioassays in female Harlan Sprague-Dawley rats to evaluate the chronic toxicity and carcinogenicity of DLCs and structurally related polychlorinated biphenyls (PCBs) and mixtures of these compounds. Mixtures of polychlorinated biphenyls (PCBs) including 3,3',4,4',5-pentachlorobiphenyl (PCB 126) and 2,3',4,4',5-pentachlorobiphenyl (PCB 118) were produced commercially before 1977 for the electric industry as dielectric insulating fluids for transformers and capacitors. Manufacture and use of these chemicals were stopped because of increased PCB residues in the environment, but they continue to be released into the environment through the use and disposal of products containing PCBs, as by-products during the manufacture of certain organic chemicals, during combustion of some waste materials, and during atmospheric recycling. This PCB mixture study was conducted as part of the dioxin TEF evaluation that includes conducting multiple 2-year rat bioassays to evaluate the relative chronic toxicity and carcinogenicity of DLCs, structurally related PCBs, and mixtures of these compounds. This study was originally a study of PCB 118 alone. However, midway through the study PCB 126 was identified as one of the minor contaminants (0.622%) of the bulk PCB 118 (98.5% pure). Given the 1,000-fold higher potency of PCB 126 for inducing dioxin-like effects (based on the TEFs for PCB 126 and PCB 118 of 0.1 and 0.0001, respectively), it was expected that the effects of administration of this compound would be due to the combined dioxin-like effects of both PCB 126 and PCB 118. Therefore, this study was reclassified as a mixture study of PCB 126 and PCB 118. 2-YEAR STUDY: Groups of female Harlan Sprague-Dawley rats were administered the PCB mixture containing PCB 126 and PCB 118 by gavage in corn oil:acetone (99:1) or vehicle alone, 5 days per week for up to 104 weeks. Dose groups are referred to by the total levels of TCDD toxic equivalents (TEQ) provided by the PCBs in the mixture in each dose group. Groups of 81 female rats were administered 7, 22, 72, or 216 ng TEQ/kg; a group of 86 female rats was administered 360 ng TEQ/kg; and a group of 81 female rats was administered the corn oil:acetone vehicle alone. Up to 10 rats per group were evaluated at 14, 31, or 53 weeks. No animals in the 360 ng TEQ/kg group were examined at 53 weeks. A group of 50 female rats was administered 360 ng TEQ/kg for 30 weeks and then the vehicle alone for the remainder of the study. Nominal doses of PCB 118 and levels of PCB 126 in each dose group used were: 7 ng TEQ/kg dose group: 62 ng/kg PCB 126 and 10 microg/kg PCB 118 7 ng TEQ/kg dose group: 62 ng/kg PCB 126 and 10 microg/kg PCB 118 22 ng TEQ/kg dose group: 187 ng/kg PCB 126 and 30 microg/kg PCB 118 72 ng TEQ/kg dose group: 622 ng/kg PCB 126 and 100 microg/kg PCB 118 216 ng TEQ/kg dose group: 1,866 ng/kg PCB 126 and 300 microg/kg PCB 118 360 ng TEQ/kg dose group: 3,110 ng/kg PCB 126 and 500 microg/kg PCB 118 No animals in the 216 or 360 ng TEQ/kg core study groups survived to the end of the study, and survival in the 360 ng TEQ/kg stop-exposure group was significantly less than in the vehicle control group. Mean body weights of 72 ng TEQ/kg rats were less than those of the vehicle controls after week 33 of the study, and mean body weights of the 216 and 360 ng TEQ/kg core study rats and the 360 ng TEQ/kg stop-exposure group rats were less than those of the vehicle controls throughout most of the study. Clinical findings related to the administration of the binary mixture of PCB 126 and PCB 118 included abnormal breathing, thinness, and ruffled hair. Thyroid Hormone Concentrations: Alterations in serum thyroid hormone levels were evaluated at the 14-, 31-, and 53-week interim evaluations. Total thyroxine (T4) and free T4 were significantly lower in most dose groups than in vehicle controls at the 14- and 31-week interim evaluations. Serum T3 was significantly lower in the 360 ng TEQ/kg group compared to vehicle controls at 31 weeks only. TSH levels were higher in the 216 and 360 ng TEQ/kg groups than in vehicle controls at 31 weeks only. Hepatic Cell Proliferation Data To evaluate hepatocyte replication, analysis of labeling of replicating hepatocytes with 5-bromo-2'-deoxyuridine was conducted at the 14-, 31-, and 53-week interim evaluations. Labeling indices were elevated at doses above 216 ng TEQ/kg at 31 weeks and at doses above 72 ng TEQ/kg at 53 weeks. Cytochrome P450 Enzyme Activities: CYP1A1-associated 7-ethoxyresorufin-O-deethylase (EROD) and CYP1A2-associated acetanilide-4-hydroxylase (A4H) activities were evaluated at the 14-, 31-, and 53-week interim evaluations to evaluate the expression of known dioxin-responsive genes. In addition, CYP2B-associated pentoxyresorufin-O-deethylase (PROD) activity was also analyzed. Hepatic and pulmonary EROD (CYP1A1) activity, hepatic A4H (CYP1A2) activity, and hepatic PROD (CYP2B1) activity were significantly greater in all dosed groups compared to the vehicle controls at weeks 14, 31, and 53. Determinations of PCB 126 and PCB 118 Concentrations in Tissues: The tissue disposition of PCB 126 and PCB 118 was analyzed in the liver, lung, fat, and blood of up to 10 rats in each group at the 14-, 31-, and 53-week interim evaluations, except for the 360 ng TEQ/kg group at 53 weeks. The tissue disposition of PCB 126 and PCB 118 was also analyzed in 10 rats per group at the end of the 2-year study in the vehicle control, 7, 22, and 72 ng TEQ/kg core study groups and the 360 ng TEQ/kg stop-exposure group. Detectable concentrations of PCB 126 and PCB 118 were observed in the liver, fat, lung, and blood. The highest levels of PCB 126 were seen in the liver whereas the highest levels of PCB 118 were seen in the fat. In general, tissue concentrations increased with increasing doses of the mixture and increasing duration of exposure. Hepatic levels of PCB 126 and PCB 118 in the 72 ng TEQ/kg group at the end of the 2-year study were 284 ng/g and 3,769 ng/g, respectively. On a TCDD equivalents basis this corresponds to 28 ng TEQ/g and 0.4 ng TEQ/g for PCB 126 and PCB 118, respectively. Cessation of administration of the mixture in the stop-exposure group led to declines in the tissue concentrations of both PCB 126 and PCB 118 to levels comparable to those observed in the 7 ng TEQ/kg group at the end of the 2-year study. Pathology and Statistical Analyses: At 14, 31, and 53 weeks, liver weights were significantly increased in treated groups with more pronounced effects occurring in the higher dose groups. At 14 weeks, hepatocyte hypertrophy and pigmentation were seen at doses less than 72 ng TEQ/kg. Exposure to the PCB mixture led to significant toxicity in the liver. At higher doses, the incidences of toxic hepatopathy were increased as indicated by increased incidences of multinucleated hepatocytes and diffuse fatty change. At 31 weeks, most rats in the 216 and 360 ng TEQ/kg groups had multiple hepatic nonneoplastic lesions. At 53 weeks all animals administered 216 ng TEQ/kg had multiple nonneoplastic lesions. The spectrum of effects and the severity of effects at the interim and 2-year time points increased with dose and duration of exposure. At the end of the 2-year study in all dosed groups, there were significantly increased incidences and severity of toxic hepatopathy characterized by hepatocyte hypertrophy, multinucleated hepatocytes, pigmentation, toxic hepatopathy, diffuse fatty change, nodular hyperplasia, centrilobular fibrosis, cholangiofibrosis, oval cell hyperplasia, bile duct cyst, bile duct hyperplasia, and portal fibrosis. There were also increased incidences of hepatocyte glandular structures, necrosis, centrilobular degeneration, eosinophilic focus, and metaplasia. The incidences of cholangiocarcinoma (multiple and/or single) were significantly increased in groups administered 22 ng TEQ/kg or greater at 2 years. The incidences of hepatocellular adenoma were also significantly increased in the 216 and 360 ng TEQ/kg core study groups. In addition, single occurrences of hepatocholangioma, cholangioma, or hepatocellular carcinoma were observed in some dosed groups administered 72 ng TEQ/kg or greater. In the lung at 53 weeks, the incidences of cystic keratinizing epithelioma and bronchiolar metaplasia were significantly increased in the 216 ng TEQ/kg group. (ABSTRACT TRUNCATED).
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PMID:Toxicology and carcinogenesis studies of a binary mixture of 3,3',4,4',5-pentachlorobiphenyl (PCB 126) (Cas No. 57465-28-8) and 2,3',4,4',5-pentachlorobiphenyl (PCB 118) (Cas No. 31508-00-6) in female Harlan Sprague-Dawley rats (gavage studies). 1734 96

N,N-dimethyl-p-toluidine was nominated for toxicology and carcinogenesis studies by the National Cancer Institute based on the potential for human exposure through its use in dental materials and bone cements and the lack of toxicity and carcinogenicity data. Male and female F344/N rats and B6C3F1/N mice were administered N,N-dimethyl-p-toluidine (greater than 99% pure) in corn oil by gavage for 3 months or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium and Escherichia coli, mouse peripheral blood, and mouse and rat liver. 3-MONTH STUDY IN RATS: Groups of 10 male and 10 female rats were administered 0, 62.5, 125, 250, 500, or 1,000 mg N,N-dimethyl-p-toluidine/kg body weight in corn oil by gavage, 5 days per week for 14 weeks. Additional groups of 10 male and 10 female rats (clinical pathology study) were administered the same doses, 5 days per week for 25 days. On day 88, blood was collected from core study rats for hemoglobin and methemoglobin analyses only. All 1,000 mg/kg male and female rats and one 500 mg/kg male rat died by study day 3. Mean body weights of all surviving dosed groups of males and females were significantly less than those of the vehicle controls. Clinical findings associated with exposure to N,N-dimethyl-p-toluidine included cyanosis, abnormal breathing, and lethargy in groups administered 250 mg/kg or greater. Methemoglobinemia appeared to be the primary hematologic toxic response, and many other lesions could be explained as secondary to methemoglobin formation including Heinz body formation; a macrocytic, hypochromic, responsive anemia; and increased hematopoietic cell proliferation in the spleen and bone marrow. In general, hematologic changes were dose-related and occurred at both evaluated timepoints in all dosed groups. Anemia was evidenced by decreases in hematocrit values, hemoglobin concentrations, and erythrocyte counts; erythrocyte macrocytosis was characterized by increases in mean cell volume and mean cell hemoglobin values; erythrocyte hypochromia was evidenced by decreases in mean cell hemoglobin concentration values; and an erythropoietic response to the anemia was characterized by substantially increased reticulocyte and nucleated erythrocyte counts. Liver weights of all surviving dosed groups of males and females were significantly greater than those of the vehicle controls. Kidney weights of all surviving dosed groups of females were significantly greater than those of the vehicle controls. There were significant decreases in left cauda epididymis and left epididymis weights in 250 mg/kg males. There was a dose-related decrease in the number of cycling females, with only four females in the 250 mg/kg group having regular cycles and females in the 125 and 250 mg/kg groups spending a significantly higher proportion of time in extended diestrus compared to the vehicle control group. In the surviving groups of rats, there were significantly increased incidences of pigmentation in the liver of all dosed groups, hepatocyte hypertrophy in groups administered 125 mg/kg or greater, and hepatocyte necrosis in 62.5, 250, and 500 mg/kg females. In the olfactory epithelium of the nose, there were dose-related increases in the incidences and severities of degeneration in all dosed groups and significantly increased incidences of metaplasia in the 250 and 500 mg/kg groups. In the respiratory epithelium of the nose, there were significantly increased incidences of hyperplasia and squamous metaplasia in all of the groups administered 125 mg/kg or greater. The incidences of glandular hyperplasia of the nose were significantly increased in males and females administered 125, 250, or 500 mg/kg. In the spleen, there were significantly increased incidences of capsule fibrosis, congestion, mesothelial hypertrophy, and lymphoid follicle atrophy primarily in groups administered 125 mg/kg or greater. Hematopoietic cell proliferation and pigmentation were increased in severity in treated groups. In the kidney, there were significantly increased incidences of nephropathy (females), pigmentation (males and females), papillary necrosis (males and females), and mineralization (males). Other treatment-related lesions included inflammation of the forestomach in males, mesenteric lymph node atrophy in females, and bone marrow hyperplasia in males and females. 3-MONTH STUDY IN MICE: Groups of 10 male and 10 female mice were administered 0, 15, 30, 60, 125, or 250 mg N,N-dimethyl-p-toluidine/kg body weight in corn oil by gavage, 5 days per week for 14 weeks. All 250 mg/kg male and female mice (except for one male mouse) died before day 10, and three males and two females administered 125 mg/kg died before the end of the study. The final mean body weight of 125 mg/kg males and the mean body weight gains of 125 mg/kg males and females were significantly less than those of the vehicle controls. Clinical findings associated with administration of N,N-dimethyl-p-toluidine included abnormal breathing, thinness, lethargy, cyanosis, and ruffled fur in 125 and 250 mg/kg males and females. Methemoglobinemia appeared to be the primary hematologic toxic response; however there were less severe erythron changes compared to the 3-month study in rats. In females, no erythron changes were detected up to 125 mg/kg. In males, inconsistent and minor decreases in hematocrit values, hemoglobin concentrations, and erythrocyte counts, and increased reticulocyte counts occurred in groups administered 60 mg/kg or greater. Methemoglobin values were minimally increased in males and females administered 30 mg/kg or greater. Heinz bodies were slightly increased in 60 mg/kg females, 125 mg/kg males and females, and the one surviving 250 mg/kg male; Heinz body formation was considered secondary to methemoglobin formation. Liver weights of all dosed groups of mice were significantly greater than those of the vehicle controls. In the surviving groups of mice, there were significantly increased incidences of bronchiolar epithelium degeneration, bronchiolar epithelium regeneration, and peribronchiolar chronic active inflammation in the lung of 125 mg/kg groups, and histiocytic infiltrates of the alveoli in 125 mg/kg females. In the nose, there were significantly increased incidences of glandular hyperplasia and olfactory epithelium metaplasia in the 125 mg/kg groups and olfactory epithelium degeneration in 60 mg/kg females and 125 mg/kg males and females. In the thymus, the incidences of thymocyte necrosis in the 125 mg/kg groups were significantly increased. In the liver, the severities of cytoplasmic vacuolization of the hepatocytes were increased in dosed groups of males and females. 2-YEAR STUDY IN RATS: Groups of 50 male and 50 female rats were administered 0, 6, 20, or 60 mg N,N-dimethyl-p-toluidine/kg body weight in corn oil by gavage, 5 days per week for 104 or 105 weeks. Additional groups of 10 male and 10 female rats (clinical pathology study) were administered the same doses for 86 days. Survival of 60 mg/kg males was significantly less than that of the vehicle controls. Mean body weights of 60 mg/kg males and females were more than 10% less than those of the vehicle controls after week 61 and week 33, respectively. Clinical findings included signs of pallor in 60 mg/kg females and hyperactivity and boxing behavior in 20 mg/kg females and 60 mg/kg males and females. The hematology findings at the 3-month timepoint were consistent with those in the 3-month study in rats which indicated that methemoglobinemia was the primary hematologic toxic response. In the 20 and 60 mg/kg groups, there were dose-related decreases in hematocrit values, hemoglobin concentrations, and erythrocyte counts. There were similar trends toward erythrocyte macrocytosis and hypochromia and increased erythropoiesis as seen in the 3-month study. While the magnitudes of the erythron decreases were not sufficient to classify the responses as anemias, the patterns of the erythron changes were identical to those in the 3-month study. In the liver of 60 mg/kg males and females, there were significantly increased incidences of hepatocellular carcinoma and hepatocellular adenoma or hepatocellular carcinoma (combined). Numerous nonneoplastic liver lesions occurred in dosed males and females primarily in the 20 and 60 mg/kg groups. In the nose, there were significantly increased incidences of transitional epithelium adenoma and transitional epithelium adenoma or carcinoma (combined) in 60 mg/kg males; transitional epithelium adenoma also occurred in female rats administered 6 or 60 mg/kg. In the nose, there were significantly increased incidences of nonneoplastic lesions in the olfactory, respiratory, and transitional epithelia of dosed rats. These lesions occurred with the greatest incidence and severity in the 60 mg/kg groups. The incidences of inflammation and nerve atrophy were significantly increased in males and females administered 60 mg/kg. There were increased incidences of follicular cell adenoma or carcinoma (combined) of the thyroid gland in all dosed groups of males, and an increased incidence of follicular cell adenoma in 20 mg/kg females. In the spleen, there were significantly increased incidences of hematopoietic cell proliferation in all dosed groups of males and females. The incidences of congestion and mesothelial hypertrophy of the capsule were significantly increased in 60 mg/kg males and all dosed groups of females. There were also significantly increased incidences of capsular fibrosis and atrophy of the lymphoid follicle in the 60 mg/kg groups. The incidences of pigmentation were significantly increased in all dosed groups of males and in 60 mg/kg females. In all dosed groups of female rats, there were significantly increased incidences of nephropathy. (ABSTRACT TRUNCATED)
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PMID:Toxicology and carcinogenesis studies of N,N-dimethyl-p-toluidine (CAS No. 99-97-8) in F344/N rats and B6C3F1/N mice (gavage studies). 2302 99