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美国国家毒理学计划(NTP)关于甲酚(化学物质登记号:95-48-7、108-39-4、106-44-5)对F344/N大鼠和B6C3F1小鼠毒性研究的技术报告(饲料研究)

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).

作者信息

Dietz Dennis

出版信息

Toxic Rep Ser. 1991 Feb;9:1-128.

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.)

摘要

甲酚是苯酚的单甲基衍生物,存在于煤焦油、各种工业溶剂和树脂以及某些香精油中。在28天毒性研究中,给F344/N大鼠和B6C3F1小鼠两性喂食浓度为300 ppm至30,000 ppm的邻甲酚、间甲酚、对甲酚或间/对甲酚(60:40)。在90天研究中,给F344/N大鼠喂食浓度高达30,000 ppm的邻甲酚或间/对甲酚(60:40),给B6C3F1小鼠喂食浓度为20,000 ppm(邻甲酚)或10,000 ppm(间/对甲酚)。在28天研究中,所有大鼠存活(每个剂量每组雌雄各5只),但一些接受30,000 ppm邻甲酚、或10,000 ppm或30,000 ppm间甲酚或对甲酚的小鼠在研究结束前死亡。在所有高剂量动物组的第一个研究周,饲料消耗量降低,在四项28天研究中,给予10,000或30,000 ppm的组体重增加通常低于对照组。给予低至3,000 ppm甲酚浓度的大鼠和小鼠,肝脏和肾脏相对重量增加。然而,这些重量增加没有一致的微观变化。骨髓发育不全以及子宫、卵巢和偶尔的乳腺萎缩主要出现在最高饮食浓度,但某些甲酚在10,000 ppm时也会出现。对甲酚和间/对甲酚研究特有的一个影响是鼻上皮和前胃的萎缩和再生变化,推测是该化学物质或其蒸气的刺激作用的直接结果。用邻甲酚和间/对甲酚进行的生殖组织评估和发情周期特征分析结果表明,对雄性生殖系统没有不良影响,但接受较高浓度邻甲酚的大鼠和小鼠以及接受间/对甲酚的大鼠发情周期延长。在90天研究中,大鼠(每个剂量每组雌雄各20只)或小鼠(每个性别和剂量10只)的死亡均不能明确归因于给予邻甲酚或间/对甲酚。在所有研究中,血液学、临床化学和尿液分析结果通常无明显异常,尽管高剂量大鼠胆汁酸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。微观分析结果与28天研究结果一致,显示给予含较高浓度邻甲酚饲料的大鼠有轻度骨髓细胞减少的证据,小鼠有前胃增生的证据。接受含间/对甲酚饲料的大鼠和小鼠有鼻刺激的证据。接受间/对甲酚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中表现出大致相似毒理学模式。3,000 ppm的饮食浓度似乎是肝脏和肾脏重量增加以及肝功能缺陷的最低影响水平。组织病理学变化,包括骨髓细胞减少、胃肠道和鼻上皮刺激以及雌性生殖器官萎缩,偶尔在10,000 ppm时出现,但在30,000 ppm高剂量时更常见。同义词:苯酚,2-甲基-(9CI);2-甲酚;邻甲酚酸;1-羟基-2-甲基苯;2-羟基甲苯;邻羟基甲苯;2-甲基苯酚;邻甲基苯酚;邻甲基苯甲醇;邻氧基甲苯;危险废物编号U052;邻甲苯酚;联合国编号2076;苯酚,3-甲基-(9CI);3-甲酚;间甲酚;间甲酚酸;1-羟基-3-甲基苯;3-羟基甲苯;间羟基甲苯;间甲酚;3-甲基苯酚;间甲基苯酚;间氧基甲苯;危险废物编号U052;间甲苯酚;联合国编号2076;苯酚,4-甲基-(9CI);4-甲酚;对甲酚酸;1-羟基-4-甲基苯;4-羟基甲苯;对羟基甲苯;对甲酚;1-甲基-4-羟基苯;对甲基羟基苯;4-甲基苯酚;对甲基苯酚;对氧基甲苯;危险废物编号U052;对甲苯酚;对甲苯醇;联合国编号2076。(注意:这些研究部分得到了《综合环境反应、赔偿和责任法》信托基金(超级基金)的资助,通过与美国公共卫生服务部有毒物质和疾病登记处的机构间协议提供。)

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