NTP technical report on the toxicity studies of Cresols (CAS Nos. 95-48-7, 108-39-4, 106-44-5) in F344/N Rats and B6C3F1 Mice (Feed Studies).

Toxicity report series Pub Date : 1991-02-01
Dennis Dietz
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Feed consumption was depressed during the first study week in all high- dose groups of animals and weight gains were generally less than controls in groups given 10,000 or 30,000 ppm in the four 28-day studies. Increased relative liver weights and kidney weights were noted in both rats and mice given concentrations of cresols as low as 3,000 ppm. However, there were no consistent microscopic changes associated with these weight increases. Bone marrow hypoplasia and uterus, ovary and occasional mammary gland atrophy were seen primarily at the highest dietary concentration, but also at 10,000 ppm with certain cresols. An effect specific to the p- cresol and m/p-cresol studies was atrophy and regenerative changes in the nasal epithelia and forestomach, presumably a direct result of the irritant effects of the chemical or its vapors. Results of reproductive tissue evaluations and estrus cycle characterizations with o-cresol and m/p-cresol gave no indication of adverse effects to the male reproductive system, but the estrus cycle was lengthened in rats and mice receiving the higher concentrations of o-cresol and rats receiving m/p-cresol. In the 90-day studies, no deaths of rats (20 per sex per dose) or mice (10 per sex and dose) could clearly be related to administration of either o-cresol or m/p-cresol. Hematology, clinical chemistry, and urinalysis results were generally unremarkable in all studies, although an accumulation of bile acids in high-dose rats was considered evidence of a deficit in hepatocellular function resulting from ingestion of the chemical. Results of microscopic analyses were consistent with findings in the 28-day studies, and revealed evidence of mild bone marrow hypocellularity in rats and forestomach hyperplasia in mice given diets containing the higher concentrations of o-cresol. Evidence of nasal irritation was present in rats and mice receiving feed containing m/p-cresol. Additional lesions in rats receiving m/p-cresol included bone marrow hypocellularity and uterine atrophy. The cresol isomers exhibited a generally similar pattern of toxicities in rats and mice. Dietary concentrations of 3,000 ppm appeared to be minimal effect levels for increases in liver and kidney weights and deficits in liver function. Histopathologic changes, including bone marrow hypocellularity, irritation to the gastrointestinal tract and nasal epithelia, and atrophy of female reproductive organs, occasionally occurred at 10,000 ppm, but were more common at the high-dose of 30,000 ppm. Synonyms: phenol, 2-methyl-(9CI); 2-cresol; o-cresylic acid; 1-hydroxy-2-methylbenzene; 2-hydroxytoluene; o-hydroxytoluene; 2-methylphenol; o-methylphenol; o-methylphenylol; o-oxytoluene; RCRA Waste Number U052; o-toluol; UN 2076; phenol, 3-methyl-(9CI); 3-cresol; m-cresole; m-cresylic acid; 1-hydroxy-3-methylbenzene; 3-hydroxytoluene; m-hydroxytoluene; m-kresol; 3-methylphenol; m-methylphenol; m-oxytoluene; RCRA Waste Number U052; m-toluol; UN 2076; phenol, 4-methyl- (9CI); 4-cresol; p-cresylic acid; 1-hydroxy-4-methylbenzene; 4-hydroxytoluene; p-hydroxytoluene; p-kresol; 1-methyl-4-hydroxybenzene; p-methylhydroxy- benzene; 4-methylphenol; p-methylphenol; p-oxytoluene; RCRA Waste Number U052; p-toluol; p-tolyl alcohol; UN 2076. (NOTE: These studies were supported in part by funds from the Comprehensive Environmental Response, Compensation, and Liability Act trust fund (Superfund) by an interagency agreement with the Agency for Toxic Substances and Disease Registry, U.S. Public Health Service.)</p>","PeriodicalId":23116,"journal":{"name":"Toxicity report series","volume":"9 ","pages":"1-128"},"PeriodicalIF":0.0000,"publicationDate":"1991-02-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Toxicity report series","FirstCategoryId":"1085","ListUrlMain":"","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 0

Abstract

Cresols are monomethyl derivatives of phenol, and are found as constituents of coal tar, in various industrial solvents and resins, and in some essential oils. In 28-day toxicity studies, F344/N rats and B6C3F1 mice of both sexes were given o-cresol, m-cresol, p-cresol, or m/p-cresol (60:40) at concentrations from 300 ppm to 30,000 ppm in the diet. In 90-day studies, o-cresol or m/p-cresol (60:40) were added to the diet in concentrations as high as 30,000 ppm to F344/N rats and 20,000 ppm (o-cresol) or 10,000 ppm (m/p-cresol) to B6C3F1 mice. In the 28-day studies, all rats survived (5 per sex per dose), but some mice given o-cresol at 30,000 ppm, or m-cresol or p-cresol at 10,000 ppm or 30,000 ppm died before the end of the studies. Feed consumption was depressed during the first study week in all high- dose groups of animals and weight gains were generally less than controls in groups given 10,000 or 30,000 ppm in the four 28-day studies. Increased relative liver weights and kidney weights were noted in both rats and mice given concentrations of cresols as low as 3,000 ppm. However, there were no consistent microscopic changes associated with these weight increases. Bone marrow hypoplasia and uterus, ovary and occasional mammary gland atrophy were seen primarily at the highest dietary concentration, but also at 10,000 ppm with certain cresols. An effect specific to the p- cresol and m/p-cresol studies was atrophy and regenerative changes in the nasal epithelia and forestomach, presumably a direct result of the irritant effects of the chemical or its vapors. Results of reproductive tissue evaluations and estrus cycle characterizations with o-cresol and m/p-cresol gave no indication of adverse effects to the male reproductive system, but the estrus cycle was lengthened in rats and mice receiving the higher concentrations of o-cresol and rats receiving m/p-cresol. In the 90-day studies, no deaths of rats (20 per sex per dose) or mice (10 per sex and dose) could clearly be related to administration of either o-cresol or m/p-cresol. Hematology, clinical chemistry, and urinalysis results were generally unremarkable in all studies, although an accumulation of bile acids in high-dose rats was considered evidence of a deficit in hepatocellular function resulting from ingestion of the chemical. Results of microscopic analyses were consistent with findings in the 28-day studies, and revealed evidence of mild bone marrow hypocellularity in rats and forestomach hyperplasia in mice given diets containing the higher concentrations of o-cresol. Evidence of nasal irritation was present in rats and mice receiving feed containing m/p-cresol. Additional lesions in rats receiving m/p-cresol included bone marrow hypocellularity and uterine atrophy. The cresol isomers exhibited a generally similar pattern of toxicities in rats and mice. Dietary concentrations of 3,000 ppm appeared to be minimal effect levels for increases in liver and kidney weights and deficits in liver function. Histopathologic changes, including bone marrow hypocellularity, irritation to the gastrointestinal tract and nasal epithelia, and atrophy of female reproductive organs, occasionally occurred at 10,000 ppm, but were more common at the high-dose of 30,000 ppm. Synonyms: phenol, 2-methyl-(9CI); 2-cresol; o-cresylic acid; 1-hydroxy-2-methylbenzene; 2-hydroxytoluene; o-hydroxytoluene; 2-methylphenol; o-methylphenol; o-methylphenylol; o-oxytoluene; RCRA Waste Number U052; o-toluol; UN 2076; phenol, 3-methyl-(9CI); 3-cresol; m-cresole; m-cresylic acid; 1-hydroxy-3-methylbenzene; 3-hydroxytoluene; m-hydroxytoluene; m-kresol; 3-methylphenol; m-methylphenol; m-oxytoluene; RCRA Waste Number U052; m-toluol; UN 2076; phenol, 4-methyl- (9CI); 4-cresol; p-cresylic acid; 1-hydroxy-4-methylbenzene; 4-hydroxytoluene; p-hydroxytoluene; p-kresol; 1-methyl-4-hydroxybenzene; p-methylhydroxy- benzene; 4-methylphenol; p-methylphenol; p-oxytoluene; RCRA Waste Number U052; p-toluol; p-tolyl alcohol; UN 2076. (NOTE: These studies were supported in part by funds from the Comprehensive Environmental Response, Compensation, and Liability Act trust fund (Superfund) by an interagency agreement with the Agency for Toxic Substances and Disease Registry, U.S. Public Health Service.)

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甲酚对F344/N大鼠和B6C3F1小鼠的毒性研究技术报告(CAS编号95-48- 7,108 -39- 4,106 -44-5)(饲料研究)。
甲酚是苯酚的单甲基衍生物,是煤焦油、各种工业溶剂和树脂以及一些精油的成分。在为期28天的毒性研究中,F344/N大鼠和B6C3F1雌雄小鼠分别以300 ppm至30,000 ppm的浓度给予邻甲酚、间甲酚、对甲酚或间/对甲酚(60:40)。在为期90天的研究中,对F344/N大鼠添加了浓度高达30,000 ppm的邻甲酚或间/对甲酚(60:40),对B6C3F1小鼠添加了浓度高达20,000 ppm(邻甲酚)或10,000 ppm(间/对甲酚)的饮食。在为期28天的研究中,所有的老鼠都存活了下来(每次剂量每只雌雄5只),但是一些老鼠在研究结束前就死亡了,它们被注射了3万ppm的邻甲酚、1万ppm的间甲酚或对甲酚。在四个为期28天的研究中,所有高剂量组的动物在第一个研究周内的饲料消耗量都有所下降,并且在给予10,000或30,000 ppm的组中,体重增加通常低于对照组。在给予低至3,000 ppm的甲酚浓度的大鼠和小鼠中,肝脏和肾脏的相对重量均有所增加。然而,这些体重增加并没有引起一致的微观变化。骨髓发育不全、子宫、卵巢和偶尔出现的乳腺萎缩主要发生在最高的膳食浓度,但也发生在10,000 ppm的某些甲酚浓度下。对甲酚和间/对甲酚研究特有的影响是鼻上皮和前胃的萎缩和再生变化,可能是化学物质或其蒸气刺激作用的直接结果。对邻甲酚和m/p-甲酚的生殖组织评估和发情周期特征的结果没有显示对雄性生殖系统的不利影响,但在接受较高浓度的邻甲酚和m/p-甲酚的大鼠和小鼠中,发情周期延长。在为期90天的研究中,没有大鼠(每性别每剂量20只)或小鼠(每性别每剂量10只)的死亡与邻甲酚或间/对甲酚的施用明显相关。在所有的研究中,血液学、临床化学和尿液分析结果一般都不显著,尽管高剂量大鼠胆汁酸的积累被认为是摄入该化学物质导致肝细胞功能缺陷的证据。显微镜分析的结果与28天的研究结果一致,并揭示了给予含有高浓度邻甲酚的饮食的大鼠轻度骨髓细胞减少和小鼠前胃增生的证据。大鼠和小鼠接受含有间/对甲酚的饲料后出现鼻腔刺激的证据。接受m/p-甲酚治疗的大鼠的其他病变包括骨髓细胞减少和子宫萎缩。甲酚异构体在大鼠和小鼠身上表现出大致相似的毒性模式。3,000 ppm的饮食浓度似乎是对肝肾重量增加和肝功能缺陷的最小影响水平。组织病理学改变,包括骨髓细胞减少、胃肠道和鼻上皮的刺激以及女性生殖器官的萎缩,在10,000 ppm时偶尔发生,但在30,000 ppm的高剂量时更为常见。同义词:苯酚,2-甲基(9CI);2-cresol;o-cresylic酸;1-hydroxy-2-methylbenzene;2-hydroxytoluene;o-hydroxytoluene;2-methylphenol;o-methylphenol;o-methylphenylol;o-oxytoluene;RCRA废物编号U052;o-toluol;联合国2076年;苯酚、3 -甲基- (9 ci);3-cresol;m-cresole;m-cresylic酸;1-hydroxy-3-methylbenzene;3-hydroxytoluene;m-hydroxytoluene;m-kresol;3-methylphenol;m-methylphenol;m-oxytoluene;RCRA废物编号U052;m-toluol;联合国2076年;苯酚4-甲基- (9CI);4-cresol;p-cresylic酸;1-hydroxy-4-methylbenzene;4-hydroxytoluene;p-hydroxytoluene;p-kresol;1-methyl-4-hydroxybenzene;p-methylhydroxy -苯;4-methylphenol;p-methylphenol;p-oxytoluene;RCRA废物编号U052;p-toluol;p-tolyl酒精;2076年联合国。(注:这些研究的部分资金来自《综合环境反应、赔偿和责任法案》信托基金(超级基金),并与美国公共卫生服务局有毒物质和疾病登记处达成了机构间协议。)
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