Gene/Protein Disease Symptom Drug Enzyme Compound
Pivot Concepts:   Target Concepts:
Query: UMLS:C0017638 (glioma)
30,880 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

The high expression of CD98 was reported in some normal tissues, including blood brain barrier, activated lymphocytes, the basal layer of skin, proximal tubles of kidney, placenta, testis and a wide variety of tumors. The CD98 complex consists of an 80-85kD heavy chain (4F2hc/FRP-1) and a 40-45kD light chain. CD98hc, 4F2hc, and FRP-1 are the same glycosylated protein each other and define antigenicity of CD98. LAT1, the sodium-independent L-type amino acid transporter 1, has been identified as a light chain of the CD98 heterodimer from C6 glioma cells. LAT1 also corresponds to TA1, an oncofetal antigen that is expressed primarily in fetal tissues and cancer cells such as glioma cells. Increased LAT1 expression was found in various malignancies including human gliomas. Several studies implicated the important role of LAT1 and 4F2hc in malignant transformation and carcinogenesis. The LAT1-CD98 pathway may represent a unique therapeutic target for cancer intervention.
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PMID:The role of CD98 in astrocytic neoplasms. 1212 61

The purpose of this review is to provide a sufficiently detailed perspective on epidemiologic studies of primary brain tumors to encourage multidisciplinary etiologic and prognostic studies among surgeons, neuro-oncologists, epidemiologists, and molecular scientists. Molecular tumor markers that predict survival and treatment response are being identified with hope of even greater gains in this area from emerging array technologies. Regarding risk factors, studies of inherited susceptibility and constitutive polymorphisms in genes pertinent to carcinogenesis (for example, DNA repair and detoxification genes and mutagen sensitivity) have revealed provocative findings. Inverse associations of the history of allergies with glioma risk observed in 3 large studies and reports of inverse associations of glioma with common infections suggest a possible role of immune factors in glioma genesis or progression. Studies continue to suggest that brain tumors might result from workplace, dietary, and other personal and residential exposures, but studies of cell phone use and power frequency electromagnetic fields have found little to support a causal connection with brain tumors; caveats remain. The only proven causes of brain tumors (that is, rare hereditary syndromes, therapeutic radiation, and immune suppression giving rise to brain lymphomas) account for a small proportion of cases. Progress in understanding primary brain tumors might result from studies of well-defined histologic and molecular tumor types incorporating assessment of potentially relevant information on subject susceptibility and environmental and noninherited endogenous factors (viruses, radiation, and carcinogenic or protective chemical exposures through diet, workplace, oxidative metabolism, or other sources). Such studies will require the cooperation of researchers from many disciplines.
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PMID:Epidemiology of primary brain tumors: current concepts and review of the literature. 1235 58

Common polymorphisms in DNA repair genes may alter protein function and an individual's capacity to repair damaged DNA; deficits in repair capacity may lead to genetic instability and carcinogenesis. To establish our overall understanding of possible in vivo relationships between DNA repair polymorphisms and the development of cancer, we performed a literature review of epidemiological studies that assessed associations between such polymorphisms and risk of cancer. Thirty studies of polymorphisms in OGG1, XRCC1, ERCC1, XPC, XPD, XPF, BRCA2, and XRCC3 were identified in the April 30, 2002 MEDLINE database (National Center for Biotechnology Information. PubMed Database: http://www.ncbi.nlm.nih.gov/entrez). These studies focused on adult glioma, bladder cancer, breast cancer, esophageal cancer, lung cancer, prostate cancer, skin cancer (melanoma and nonmelanoma), squamous cell carcinoma of the head and neck, and stomach cancer. We found that a small proportion of the published studies were large and population-based. Nonetheless, published data were consistent with associations between: (a) the OGG1 S326C variant and increased risk of various types of cancer; (b) the XRCC1 R194W variant and reduced risk of various types of cancer; and (c) the BRCA2 N372H variant and increased risk of breast cancer. Suggestive results were seen for polymorphisms in other genes; however, small sample sizes may have contributed to false-positive or false-negative findings. We conclude that large, well-designed studies of common polymorphisms in DNA repair genes are needed. Such studies may benefit from analysis of multiple genes or polymorphisms and from the consideration of relevant exposures that may influence the likelihood of cancer in the presence of reduced DNA repair capacity.
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PMID:Polymorphisms in DNA repair genes and associations with cancer risk. 1249 39

Bromoethane is an alkylating agent used primarily as a chemical intermediate in various organic syntheses. In toxicology and carcinogenesis studies, groups of F344/N rats and B6C3F1 mice of each sex received whole-body exposure to bromoethane (greater than 98% pure) once for 4 hours or for 6 hours per day, 5 days per week, for 14 days, 14 weeks, or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium and Chinese hamster ovary (CHO) cells. Single-Exposure, Fourteen-Day, and Fourteen-Week Studies: Single-exposure inhalation studies were conducted in rats and mice at target concentrations of 625, 1,250, 2,500, 5,000, or 10,000 ppm bromoethane. All rats exposed to 10,000 ppm bromoethane and 3/5 female rats exposed to 5,000 ppm died before the end of the single-exposure studies. All mice exposed to 5,000 or 10,000 ppm bromoethane and 2/5 female mice exposed to 1,250 ppm died before the end of the studies. Fourteen-day inhalation studies were conducted in rats and mice at target concentrations of 0, 250, 500, 1,000, 2,000, or 4,000 ppm bromoethane. All rats and mice exposed to 2,000 or 4,000 ppm died before the end of the 14-day studies. Final mean body weights of exposed and control rats were similar. Fourteen-week inhalation studies were conducted in rats and mice at target concentrations of 0, 100, 200, 400, 800, or 1,600 ppm bromoethane. Four of 10 male and 2/10 female rats exposed to 1,600 ppm died before the end of the 14-week studies. The final mean body weights of rats exposed to 1,600 ppm were lower than the initial mean body weights. Compound-related lesions observed in rats at 1,600 ppm, but not at lower concentrations, included minimal atrophy of the thigh muscle, minimal-to-moderate multifocal mineralization in the cerebellum of the brain, minimal-to-severe hemosiderosis of the spleen, marked atrophy of the testis, and minimal-to- mild atrophy of the uterus. The effects in the testis and uterus are probably due to chemical-related loss in body weight during the studies. In mice, compound-related deaths included 3/10 male and 1/10 female mice exposed to 1,600 ppm, 1/9 males exposed to 800 ppm, and 1/10 males exposed to 400 ppm. The final mean body weights of male and female mice exposed to 1,600 ppm were about 15% lower than those of controls. Compound-related effects included atrophy of the uterus and involution of the ovary in females exposed to 1,600 ppm bromoethane. Based on these results, 2-year studies were conducted by exposing groups of 49 or 50 rats or mice of each sex to bromoethane at 0, 100, 200, or 400 ppm, 6 hours per day, 5 days per week. Body Weight and Survival in the Two-Year Studies: Mean body weights of exposed and control rats were generally similar throughout the studies. No significant differences in survival were observed between any groups of male rats (control, 17/49; 100 ppm, 26/50; 200 ppm, 27/50; 400 ppm, 21/50); survival of the 100-ppm group of female rats was greater than that of controls (19/50; 29/50; 24/49; 23/50), and the number of control and 400-ppm male rats and control female rats surviving to the end of the studies was low. Mean body weights of the 400-ppm group of male mice were up to 9% lower than those of controls throughout the study. Mean body weights of the 400-ppm group of female mice were generally 6%-16% lower than those of controls after week 29. No differences in survival were observed between any group of male mice (35/50; 37/50; 30/50; 34/50). The survival of the 400-ppm group of female mice was lower than that of controls at the end of the study (36/50; 37/50; 37/49; 23/49). Nonneoplastic and Neoplastic Effects in the Two-Year Studies: The incidences of pheochromocytomas or malignant pheochromocytomas (combined) of the adrenal medulla were increased in exposed male rats (control, 8/40; 100 ppm, 23/45; 200 ppm, 18/46; 400 ppm, 21/46). Granular cell neoplasms of the brain were seen in exposed male rats but not in controls (0/49; 3/50; 1/50; 1/50). A glioma, an astrocytoma, or an oligodendroglioma was seen in 3/50 male rats exposed to 100 p in 3/50 male rats exposed to 100 ppm. Gliomas were not observed in control female rats, but they occurred in exposed female rats with a significant positive trend (0/50; 1/50; 1/48; 3/50). The historical incidence of granular cell tumors in male F344/N rat chamber controls at the study laboratory is 0/297. The incidences of gliomas in the exposed female groups were not significantly greater than that in the controls and were within the historical incidence range for glial cell neoplasms for untreated controls in NTP studies (mean: 23/1,969, 1%; range: 0/50-3/50), but they exceeded the historical incidence range for chamber controls at the study laboratory (mean: 1/297, 0.3%; range: 0/50-1/50). Alveolar epithelial hyperplasia was increased in rats exposed to 400 ppm bromoethane (male: 3/48; 7/49; 7/48; 18/48; female: 5/50; 4/48; 5/47; 10/49). Alveolar/bronchiolar adenomas or carcinomas (combined) were seen in four male rats exposed to 200 ppm and in one exposed to 400 ppm. Alveolar/bronchiolar adenomas were observed in 3/49 female rats at 400 ppm but not at lower concentrations or in controls. The incidences in exposed male and female rats were not significantly greater than those in controls; however, the historical incidence in rat chamber controls for alveolar/bronchiolar adenomas or carcinomas (combined) at the study laboratory is 6/299 (2%) for males and 4/297 (1.3%) for females. The incidences of epithelial hyperplasia and squamous metaplasia of the nasal cavity were increased in rats exposed to 400 ppm. The incidence of suppurative inflammation of the nasal cavity was increased in exposed male rats, and the incidences of suppurative inflammation of the larynx and metaplasia of the olfactory sensory epithelium were increased in exposed male and female rats. An adenoma of the nose was seen in one 400-ppm male rat and in one 400-ppm female mouse. Suppurative inflammation and dilatation of the salivary gland ducts were observed at increased incidences in the 200- and 400-ppm groups of female rats. Animals were found to be positive for rat coronavirus/sialodacryoadenitis virus antibodies. The incidence of mammary gland neoplasms was significantly lower in female rats at 400 ppm than in controls (18/50; 15/50; 10/48; 7/50). Adenomas (0/50; 1/50; 1/47; 6/48), adenocarcinomas (0/50; 2/50; 3/47; 19/48), and squamous cell carcinomas (0/50; 1/50; 1/47; 3/48) of the uterus occurred in exposed female mice and not in control mice. The incidence of alveolar/bronchiolar neoplasms was greater in male mice at 400 ppm than in controls (adenomas or carcinomas, combined: 7/50; 6/50; 12/50; 15/50). Acute/chronic inflammation of the lung was observed at increased incidences in female mice at 200 and 400 ppm. Genetic Toxicology: Bromoethane, tested in a closed environment of a desiccator, was mutagenic in S. typhimurium strain TA100 with and without exogenous metabolic activation; it was not mutagenic in strain TA98. In cultured CHO cells, bromoethane induced sister chromatid exchanges (SCEs) but not chromosomal aberrations in both the presence and absence of exogenous metabolic activation. Conclusions: Under the conditions of these 2-year inhalation studies, there was some evidence of carcinogenic activity of bromoethane for male F344/N rats, as indicated by increased incidences of pheochromocytomas of the adrenal gland; neoplasms of the brain and lung may also have been related to exposure to bromoethane. For female F344/N rats, there was equivocal evidence of carcinogenic activity, as indicated by marginally increased incidences of neoplasms of the brain and lung. For male B6C3F1 mice, there was equivocal evidence of carcinogenic activity, based on marginally increased incidences of neoplasms of the lung. There was clear evidence of carcinogenic activity for female B6C3F1 mice, as indicated by neoplasms of the uterus. Synonyms: monobromoethane; bromic ether; hydrobromic ether
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PMID:Toxicology and Carcinogenesis Studies of Bromoethane (Ethyl Bromide) (CAS No. 74-96-4) in F344/N Rats and B6C3F1 Mice (Inhalation Studies). 1269 78

Diphenhydramine hydrochloride is a widely used antihistaminic drug in human and veterinary medicine. Toxicology and carcinogenesis studies were conducted by feeding diets containing USP-grade diphenhydramine hydrochloride (greater than 99% pure) to groups of F344/N rats and B6C3F1 mice of each sex for 14 days, 13 weeks, or 2 years. Genetic toxicology studies were conducted in Salmonella typhimurium, mouse L5178Y cells, and Chinese hamster ovary (CHO) cells. Fourteen-Day and Thirteen-Week Studies: In the 14-day studies, dietary concentrations ranged from 620 to 10,000 ppm for rats and from 310 to 5,000 ppm for mice. All rats that received diets containing 10,000 ppm and 9/10 rats that received diets containing 5,000 ppm died before the end of the studies. The final mean body weights of rats receiving 1,250 or 2,500 ppm were 12%-13% or 30%-34% lower than those of controls. Feed consumption by rats at the three highest concentrations was more than 30% less than that by controls. All mice receiving 5,000 ppm, 4/5 males and 4/5 females receiving 2,500 ppm, and 4/5 males receiving 1,250 ppm died before the end of the studies. The final mean body weights of mice that received 1,250 or 2,500 ppm were lower than the initial weights. All dosed rats and mice were hyperactive and sensitive to sound and/or touch. In the 13-week studies, dietary concentrations of diphenhydramine hydrochloride ranged from 156 to 2,500 ppm for rats and from 78 to 1,250 ppm for mice. All rats lived to the end of the studies. The final mean body weights of rats receiving 1,250 or 2,500 ppm were about 15% or 35% lower than those of controls. The final mean body weight of female rats receiving 625 ppm was 9% lower than that of controls. Increased activity was observed for all male and female rats receiving 1,250 and 2,500 ppm. Cytoplasmic vacuolization of the liver, characteristic of fat accumulation, was observed in male and female rats receiving 313-2,500 ppm. The severity of this change increased with increased dose. For mice, 1/10 males receiving 313 ppm, 2/10 males receiving 625 ppm, and 8/10 males receiving 1,250 ppm died before the end of the studies. The final mean body weights of mice that received 625 or 1,250 ppm were about 9% or 16% lower than those of controls. No compound-related histopathological effects were observed in mice. Based on the mortality and body weight effects of diphenhydramine hydrochloride in the short-term studies, dietary concentrations selected for the 2-year studies were 0,313, and 635 ppm diphenhydramine hydrochloride for male rats and 0, 156, and 313 ppm for female rats and male and female mice. Body Weight and Survival in the Two-Year Studies: Mean body weights of dosed and control rats were similar throughout the studies, and mean body weights of dosed mice were 3%-13% lower than those of controls throughout most of the studies. No significant differences in survival were observed between any groups of rats or mice of either sex (male rats: control, 29/50; low dose, 32/50; high dose, 24/50; female rats: 35/50; 32/50; 36/50; male mice: 29/50; 30/50; 24/48; female mice: 37/50; 39/50; 32/50). The estimated average daily feed consumption by dosed rats and dosed mice was similar to that by controls. The average amount of diphenhydramine hydrochloride consumed per day was approximately 13 or 27 mg/kg for low dose or high dose male rats, 7 or 15 mg/kg for low dose or high dose female rats, and 21 or 46-47 mg/kg for low dose or high dose male and female mice. Nonneoplastic and Neoplastic Effects in the Two-Year Studies: For three high dose male rats, astrocytomas were found in brain sections taken by routine sampling procedures. Gliomas, containing neoplastic astrocytes and oligodendrocytes, were found in one control and one additional high dose male rat. The incidence of glial cell tumors in high dose male rats (4/50) exceeded the highest incidence in historical controls in the Program (2/50). The historical incidence of glial cell tumors is less than 0.7% in approximately 2,000 untreated control male F344/N rats. Three addiless than 0.7% in approximately 2,000 untreated control male F344/N rats. Three additional sections of brain were prepared from the residual fixed tissues of each male and female rat. One additional astrocytoma in a high dose male rat and one astrocytoma in a high dose female rat were observed in these sections. Adenomas of the anterior pituitary gland in female rats occurred with a significant positive trend; the incidences in low dose male and high dose female rats were marginally greater than those in controls (male: control, 11/49; low dose, 21/50; high dose, 14/49; female: 23/50; 26/50; 35/50). The incidence of alveolar/bronchiolar adenomas in low dose male rats was slightly greater than that in controls (0/49; 5/50; 3/50). The incidences of alveolar/bronchiolar adenomas or carcinomas (combined) in dosed male rats were not significantly different from that in controls (1/49; 6/50; 5/50) but exceeded the highest incidence in historicalcontrols (4/49). The historical incidence of alveolar/bronchiolar neoplasms in untreated control male F344/N rats is approximately 2.2%. Adenomatous hyperplasia of the lung was not increased in incidence in dosed male rats compared with controls. The incidences of granulomas of the liver were increased in dosed rats (male: 0/49; 3/50; 4/50; female: 8/50; 15/49; 18/50). At no site were the incidences of neoplastic lesions in dosed mice considered to be compound related. Cytoplasmic vacuolization (fatty metamorphosis) of the liver was observed at an increased incidence in high dose female mice (0/49; 1/49; 8/49). Genetic Toxicology: Diphenhydramine hydrochloride was not mutagenic in S. typhimurium strains TA98, TA100, TA1535, or TA1537 when tested in either the presence or absence of exogenous metabolic activation. Exposure to this chemical did not induce trifluorothymidine (Tft) resistance in mouse L5178Y lymphoma cells with or without metabolic activation. In cytogenetic tests with cultured CHO cells, diphenhydramine hydrochloride induced chromosomal aberrations in the absence, but not the presence, of exogenous metabolic activation (S9); no induction of sister chromatid exchanges (SCEs) was observed in these cells with or without S9. Conclusions: Under the conditions of these 2-year feed studies, there was equivocal evidence of carcinogenic activity of diphenhydramine hydrochloride for male F344/N rats, based on marginally increased incidences of uncommon brain neoplasms (astrocytomas or gliomas) and of alveolar/bronchiolar neoplasms. There was equivocal evidence of carcinogenic activity for female F344/N rats, based on a marginal increase in the incidence of pituitary gland adenomas. There was no evidence of carcinogenic activity for male or female B6C3F1 mice fed diets containing 156 or 313 ppm diphenhydramine hydrochloride. Synonyms: 2-diphenylmethoxy-N,N-dimethylethanamine hydrochloride; 2-(benzhydryloxy)-N,N-dimethylethylamine hydrochloride; b-dimethylaminoethyl benzhydryl ether hydrochloride; benzhydramine hydrochloride Trade Names: Alleran; Benadryl
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PMID:NTP Toxicology and Carcinogenesis Studies of Diphenhydramine Hydrochloride (CAS No. 147-24-0) in F344/N Rats and B6C3F1 Mice (Feed Studies). 1270 39

4-Hexylresorcinol, which is used as an anthelmintic and antiseptic, was nominated by the National Cancer Institute for study. Toxicology and carcinogenesis studies were conducted by administering 4-hexylresorcinol (greater than 99% pure) in corn oil by gavage to groups of F344/N rats and B6C3F1 mice of each sex for 16 days, 13 weeks, or 2 years. Sixteen-Day and Thirteen-Week Studies: In the 16-day studies, groups of five rats and five mice of each sex were administered 0, 31.3, 62.5, 125, 250, or 500 mg/kg 4-hexylresorcinol. Survival was not affected. Decreased body weights were seen in male rats that received 250 or 500 mg/kg 4-hexylresorcinol. No other effects were observed. In the 13-week studies, groups of 10 rats and 10 mice of each sex were administered 0, 62.5, 125, 250, 500, or 1,000 mg/kg of the chemical, 5 days per week. All rats and male mice and 9/10 female mice that received 1,000 mg/kg died before the end of the studies. Final mean body weights of male rats that received 250 or 500 mg/kg were 22% or 38% lower than that of the vehicle controls; final mean body weights of female rats that received 250 or 500 mg/kg were 16% or 9% lower. No compound-related gross or microscopic pathologic effects were observed in rats. No body weight effects were observed for mice. Mild to moderate nephropathy was dose related in male and female mice. Based on these results, 2-year toxicology and carcinogenesis studies of 4-hexylresorcinol were conducted by administering 0, 62.5, or 125 mg/kg to groups of 50 F344/N rats and 50 B6C3F1 mice of each sex, 5 days per week. Body Weight and Survival in the Two-Year Studies: Mean body weights of high dose male rats were 7%-11% lower than those of the vehicle controls throughout the study. Mean body weights of low dose male and dosed female rats were similar to those of the vehicle controls. The body weights of dosed male and dosed female mice were comparable to those of vehicle controls except during the last 16 weeks of the studies, when body weights were 6%-16% lower in the dosed groups. No significant differences in survival were observed between any groups of rats or mice of either sex (male rats: vehicle control, 30/50; low dose, 29/50; high dose, 33/50; female rats: 28/50; 32/50; 30/50; male mice: 36/50; 26/50; 30/50; female mice: 35/50; 32/50; 35/50). Nonneoplastic and Neoplastic Lesions in the Two-Year Studies: Two astrocytomas and an oligodendroglioma were observed in high dose male rats, a glioma was observed in one low dose male rat, and an oligodendroglioma was observed in one vehicle control male rat. These neoplasms were not considered to be related to 4-hexylresorcinol administration. Focal medullary hyperplasia of the adrenal gland was observed at increased incidences in dosed male mice (5/50; 16/50; 10/49). Pheochromocytomas in male mice occurred with a marginal upward trend (1/50; 2/50; 5/49). Historically, these neoplasms are observed in about 1% of corn oil vehicle control B6C3F1 male mice. The incidences of neoplasms of the harderian gland in male mice were slightly increased over those in the vehicle controls (adenomas or carcinomas, combined: 0/50; 4/50; 3/50). Decreases were observed in the incidences of mononuclear cell leukemia in dosed male (12/49; 7/50; 1/50) and female (16/50; 3/50; 2/50) rats, hepatocellular adenomas or carcinomas (combined) in dosed male mice (21/50; 9/50; 9/50), and circulatory system tumors in male (10/50; 4/50; 2/50) and female (6/50; 2/49; 0/50) mice. These decreased incidences of tumors in rats and mice are considered to be possibly related to 4-hexylresorcinol administration. The incidences and severity of nephropathy (male: 39/50; 43/50; 47/50; female: 7/50; 40/49; 47/50) and incidences of osteosclerosis (male: 5/50; 5/50; 15/50; female: 21/50; 25/49; 40/50) were increased in both dosed male and female mice and are considered to be related to chemical exposure. Genetic Toxicology: 4-Hexylresorcinol was not mutagenic for Salmonella typhimurium strains TA98, TA100, TA1535, or TA1537 with or without S9 metabolic activation. 4-Hexylre, TA1535, or TA1537 with or without S9 metabolic activation. 4-Hexylresorcinol induced forward mutations at the TK locus in mouse L5178Y cells in the presence of S9; no response was observed in the absence of metabolic activation. In cytogenetic assays with cultured Chinese hamster ovary (CHO) cells, 4-hexylresorcinol caused an increase in the frequency of sister chromatid exchanges (SCEs) in the absence of metabolic activation; no induction of SCEs was observed in the presence of S9. Chromosomal aberrations were not induced in CHO cells with or without metabolic activation. Data Audit: The data, documents, and pathology materials from the 2-year studies of 4-hexylresorcinol were audited at the NTP Archives. The audit findings show that the conduct of the studies is documented appropriately and support the data and results given in this Technical Report. Conclusions: Under the conditions of these 2-year gavage studies, there was no evidence of carcinogenic activity of 4-hexylresorcinol for male or female F344/N rats given doses of 62.5 or 125 mg/kg. There was equivocal evidence of carcinogenic activity of 4-hexylresorcinol for male B6C3F1 mice, as shown by marginally increased incidences of pheochromocytomas (and hyperplasia) of the adrenal medulla and of harderian gland neoplasms. There was no evidence of carcinogenic activity for female B6C3F1 mice given doses of 62.5 or 125 mg/kg 4-hexylresorcinol. Decreased incidences of three tumors types were considered related to 4-hexylresorcinol administration: mononuclear cell leukemia in male and female rats, hepatocellular neoplasms in male mice, and circulatory system tumors in male and female mice. Synonyms: 4-hexyl-1,3-benzenediol; 4-hexyl-1,3-dihydroxybenzene
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PMID:NTP Toxicology and Carcinogenesis Studies of 4-Hexylresorcinol (CAS No. 136-77-6) in F344/N Rats and B6C3F1 Mice (Gavage Studies). 1273 6

1,3-Butadiene is used as an intermediate in the production of elastomers, polymers, and other chemicals. Of the 1,3-butadiene used in 1978, 44% was used to manufacture styrene-butadiene rubber (a substitute for natural rubber, produced by copolymerization of 1,3-butadiene with styrene), and 19% was used to produce polybutane elastomer (a substance that increases resistance of tire products to wear, heat degradation, and blowouts). Chloroprene monomer, derived from 1,3-butadiene, is used exclusively to manufacture neoprene elastomers for non-tire and latex applications. Commercial nitrile rubber, used largely in rubber hoses, seals, and gaskets for automobiles, is a copolymer of 1,3-butadiene and acrylonitrile. Acrylonitrile- butadiene- styrene resins, usually containing 20%-30% 1,3-butadiene by weight, are used to make parts for automobiles and appliances. Other polymer uses include specialty polybutadiene polymers, thermoplastic elastomers, nitrile barrier resins, and K resins(R). 1,3-Butadiene is used as an intermediate in the production of a variety of industrial chemicals, including two fungicides, captan and captofol. It is approved by the U.S. Food and Drug Administration for use in the production of adhesives used in articles for packaging, transporting, or holding food; in components of paper and paperboard that are in contact with dry food; and as a modifier in the production of semigrid and rigid vinyl chloride plastic food-contact articles. No information was located on the levels of monomer or on its elution rate from any of the commercially available polymers. It is not known if unreacted 1,3-butadiene migrated from packaging materials. Male and female B6C3F1 mice were exposed to air containing 1,3-butadiene (greater than 99% pure) at concentrations of 0-8,000 ppm in 15-day and 14-week inhalation studies. In the 15-day studies, survival was unaffected by dose, and no pathologic effects were observed; slight decreases in mean body weight occurred at the high concentrations. In the 14-week studies, mean body weight gain decreased with dose, and survival in the 5,000-ppm and 8,000-ppm groups of males was markedly reduced; no other compound-related effects were reported. Inhalation carcinogenesis studies of 1,3-butadiene were conducted by exposing groups of 50 male and female B6C3F1 mice 6 hours per day for 5 days per week to air containing the test chemical at concentrations of 0 (chamber controls), 625, or 1,250 ppm. These studies were planned for 103-week exposures but were terminated at week 60 for male mice and week 61 for female mice because of the rapidly declining survival, primarily due to neoplasia. Body weights were not affected by 1,3-butadiene. Significantly increased incidences of neoplasms at multiple sites were observed in mice exposed to 1,3-butadiene. Hemangiosarcomas of the heart occurred at increased incidences in exposed males and females (male: control, 0/50; low dose, 16/49; high dose, 7/49; female: 0/50; 11/48; 18/49). Hemangiosarcomas were also observed in the peritoneal cavity (one high dose male), subcutaneous tissue (two low dose females), and liver (one high dose female). Malignant lymphomas, diagnosed as early as week 20, were observed at increased incidences in exposed male and female mice (male: 0/50; 23/50; 29/50; female: 1/50; 10/49; 10/49). Alveolar/bronchiolar adenomas and alveolar/bronchiolar (both separately and combined) occurred at increased incidences in exposed male and female mice (combined incidences -- male: 2/50; 14/49; 15/49; female: 3/49; 12/48; 23/49). Epithelial hyperplasia of the forestomach occurred at increased incidences in dosed mice (male: 0/49; 5/40; 7/44; female: 0/49; 5/42; 9/49). Papillomas of the forestomach occurred in low dose male and in low dose and high dose female mice (male: 0/49; 5/40; 0/44; female: 0/49; 4/42; 10/49). Squamous cell carcinomas of the forestomach were observed in dosed mice (male: 0/49, 2/40, 1/44; female: 0/49, 1/42, 1/49). Acinar cell carcinomas of the mammary gland were observed at an increased incidence in high dose female reased incidence in high dose female mice (0/50; 2/49; 6/49); adenosquamous carcinomas were found in four low dose females. The incidences of granulosa cell tumors of the ovary were increased in dosed females (0/49; 6/45; 12/48). A granulosa cell carcinoma was observed in another high dose female. Gliomas were observed in two 68- to 69-week-old low dose and one high dose male mice; brain tumors are uncommon even in 2-year old mice. Liver necrosis occurred at increased incidences in dosed male and low dose female mice (male; 1/50, 8/49, 8/49; female: 6/50, 15/47, 6/49). Hepatocellular adenomas or carcinomas (combined) were observed at an increased incidence in high dose female mice (0/50, 2/47 5/49). No neoplastic lesions of the nasal cavity were observed at any dose level. The following nonneoplastic lesions of the nasal cavity occurred in mice exposed at 1,250 ppm: chronic inflammation (male, 35/50; female, 2/49); fibrosis (male, 33/50; female, 2/49); cartilaginous metaplasia (male, 16/50; female, 1/49); osseous metaplasia (male, 11/50; female, 2/49); and atrophy of the sensory epithelium (male, 32/50). No nonneoplastic lesions of the nasal cavity were found in the controls. The incidence of testicular atrophy (0/50, 19/49, 11/48) or ovarian atrophy (2/49, 40/45, 40/48) was increased in exposed male or female mice. An audit of the experimental data from these studies on 1,3-butadiene was conducted by the National Toxicology Program. No data discrepancies were found that influenced the final interpretation of these experiments. Under the conditions of these studies, there was clear evidence of carcinogenicity for 1,3-butadiene in male and female B6C3F1 mice, as shown by increased incidences and early induction of hemangiosarcomas of the heart, malignant lymphomas, alveolar/bronchiolar adenomas and carcinomas, and papillomas of the stomach in males and females; and of acinar cell carcinomas of the mammary gland, granulosa cell tumors of the ovary, and hepatocellular adenomas and adenomas or carcinomas (combined) in females. 1,3-Butadiene was associated with nonneoplastic lesions in the respiratory epithelium, liver necrosis, and testicular or ovarian atrophy. Synonyms: butadiene; biethylene; bivinyl; divinyl; erythrene; vinylethylene; pyrrolylene
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PMID:NTP Toxicology and Carcinogenesis Studies of 1,3-Butadiene (CAS No. 106-99-0) in B6C3F1 Mice (Inhalation Studies). 1274 15

Propyl gallate is a white to nearly white odorless powder having a slightly bitter taste. Solutions of propyl gallate turn dark in the presence of iron or iron salts. Propyl gallate has been used since 1948 as an antioxidant to stabilize cosmetics, food packaging materials, and foods containing fats. As an additive, it may be found in edible fats, oils, mayonnaise, shortening, baked goods, candy, dried meat, fresh pork sausage, and dried milk, and it is used in hair grooming products, pressure-sensitive adhesives, lubricating oil additives, and transforming oils. A NTP Carcinogenesis bioassay of propyl gallate was conducted by feeding diets containing 6,000 or 12,000 ppm propyl gallate to groups of 50 F344/N rats and 50 B6C3F1 mice of each sex for 103 weeks. Groups of 50 untreated rats and 50 untreated mice of each sex served as controls. Survival of rats and mice was not adversely affected by propyl gallate, but mean body weights of dosed rats and mice of each sex were lower than those of the controls. At 104 weeks, mean body weights of low-and high-dose rats were 4% and 8% lower than those of the controls for males and 11% and 19% lower than those of the controls for females. Similarly, mean body weights of low-and high-dose mice were 5% and 8% lower than those of the controls for males and 11% (both dose groups) lower than those of the controls for females. Thyroid follicular-cell adenomas or carcinomas (combined) occurred in male rats with a statistically significant (P<0.05) positive trend, but the incidences in the dosed groups were not statistically significant in direct comparisons with the control groups. Moreover, the incidence of high-dose male rats with follicular-cell tumors (3/50, 6%) was not statistically different from the historical control rate (14/584, 2.4%) for the laboratory that conducted this bioassay. Rare tumors (an astrocytoma or a glioma) were found in the brains of two low-dose female rats. The incidence of all brain tumors in the Bioassay Program is only 0.86%. The absence of this tumor in the high-dose female rat group reduces the likelihood that this tumor is related to propyl gallate administration. Increased incidences of hepatic cytoplasmic vacuolization and suppurative inflammation of the prostate were observed in dosed male rats. These findings were considered to be related to administration of propyl gallate. Tumors (mostly benign) of the preputial gland, islet-cell tumors of the pancreas, and pheochromocytomas of the adrenal gland were observed with significantly (P<0.05) higher incidences in the low- dose male rats, but there was little evidence of an effect in the high-dose group. The incidences of male rats with tumors of the preputial gland were 1/50 (2%) for controls, 8/50 (16%) for the low-dose, and 0/50 (0%) for the high-dose group. Islet-cell tumors of the pancreas occurred in 2/50 (4%) control males, 9/50 (18%) low-dose males, and 4/50 (8%) for high-dose males. Pheochromocytomas of the adrenal gland were observed in 4/50 (8%) control males, 13/48 (25%) low-dose males, and 8/50 (16%) high-dose males. Negative trends (P<0.05) were observed for leukemia in male rats (16/50, 7/50, 6/50) and for fibroadenomas of the mammary gland in female rats (11/50, 2/50, 5/50). In male mice, malignant lymphoma was observed with a significantly (P</=0.014) positive trend (control, 1/50, 2%; low-dose, 3/49, 6%; high-dose, 8/50, 16%), and the incidence in the high-dose group was significantly (P</=0.028) higher than that observed in the concurrent controls. However, the high-dose incidence was not statistically different from the historical rate (60/640, 9.4%) for the laboratory that conducted this bioassay. Adenomas of the liver in female mice occurred with a statistically significant (P</=0.022) positive trend, and the incidence in the high-dose group was significantly (P</=0.039) higher than that of the controls (0/50, 0%; 2/50, 4%; 5/49, 10%). The incidences of hepatocellular adenomas or carcinomas (combined) were similar in control and dosed groups (3/50, 6%; 3/50, 6%; 5/49, 10%). Negative&percnt;; 2/50, 4&percnt;; 5/49, 10&percnt;). The incidences of hepatocellular adenomas or carcinomas (combined) were similar in control and dosed groups (3/50, 6&percnt;; 3/50, 6&percnt;; 5/49, 10&percnt;). Negative trends (P&lt;0.05) were obtained for fibromas of the skin or subcutaneous tissue in male mice (5/50, 1/49, 0/50). Under the conditions of this bioassay, propyl gallate was not considered carcinogenic for F344/N rats, although there was evidence of an increased proportion of low-dose male rats with preputial gland tumors, islet-cell tumors of the pancreas, and pheochromocytomas of the adrenal glands; rare tumors of the brain occurred in two low-dose females. Propyl gallate was not considered to be carcinogenic for B6C3F1 mice of either sex, although the increased incidence of malignant lymphoma in male mice may have been related to the dietary administration of propyl gallate. Levels of Evidence of Carcinogenicity: Male Rats: Equivocal Female Rats: Negative Male Mice: Equivocal Female Mice: Negative Synonyms: 2,4,5 trihydroxybenzoic acid propyl ester; gallic acid propyl ester; Progallin P; Tennox PG
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PMID:NTP Carcinogenesis Bioassay of Propyl Gallate (CAS No. 121-79-9) in F344/N Rats and B6C3F1 Mice (Feed Study). 1275 Jul 52

The most severe form of brain glioma, glioblastoma (GBM), is highly malignant and usually resistant to chemotherapy. Therefore, discovery of new targets for gene therapy is important. Using subtraction cloning, we identified the human N-Myc downstream-regulated gene 2 (hNDRG2), located at chromosome 14q11.2, as a gene that is significantly suppressed in GBM tissues. Semiquantitative RT-PCR showed that the hNDRG2 gene transcript is expressed in normal brain tissue and low-grade gliomas but is present at low levels in 15 of 27 (56%) human GBM tissues and all of the 6 human glioblastoma cell lines examined. Furthermore, transfection of human glioblastoma U373 and U138 cells with a cDNA encoding hNDRG2 markedly reduced the cell proliferation. Our findings provide the first evidence to suggest that hNDRG2 may play a role in glioblastoma carcinogenesis.
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PMID:N-Myc downstream-regulated gene 2 (NDRG2) inhibits glioblastoma cell proliferation. 1284 71

The mechanisms of carcinogenesis in nervous tissues are not well understood. It is now established that adenosine 3,',5'-cyclic monophosphate (cAMP)-pathway plays a crucial role in initiating differentiation in transformed and embryonic cells of neuronal and glial origin. Therefore, we propose that defects in the cAMP-pathway may initiate the first phase of carcinogenesis (immortalization). Subsequent genetic abnormalities in oncogenes, anti-oncogenes or other cellular genes individually or in combination may lead to transformation (cancer phenotype). This hypothesis is derived from the fact that an elevation of the cAMP level in murine NB cells induces terminal differentiation in many of these cells in spite of the fact that they are highly aneuploid. Additional changes in cAMP-regulated genes responsible for initiating differentiation may make these cells resistant to cAMP or may make the cAMP-effect on differentiation reversible. Indeed, cAMP-resistant cells exist in NB cell populations, and the cAMP-effect on differentiation is reversible in glioma cells. Identification of genes that initiate, promote and maintain terminal differentiation and those which prevent differentiation following elevation of cAMP in NB cells may increase our understanding of the mechanisms of carcinogenesis. This review illustrates the following: (a) historical background leading to the discovery of cAMP as an inducer of differentiation in nerve cells; (b) identification of potential sites in cAMP-pathway that may play a crucial role in initiating the first phase of carcinogenesis (immortalization) and potential gene targets in immortalized cells whose alterations may cause neoplastic transformation of nerve cells. It is interesting to note that the cAMP pathway remains responsive to an elevated cAMP level in inducing differentiation in NB cells in spite of chromosomal anomalies and genetic changes associated with the maintenance of a cancer phenotype.
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PMID:Defects in cAMP-pathway may initiate carcinogenesis in dividing nerve cells: a review. 1457 64


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