NTP toxicology and carcinogenesis studies of decalin (CAS No. 91-17-8) in F344/N rats and B6C3F(1) mice and a toxicology study of decalin in male NBR rats (inhalation studies).

Q4 Medicine National Toxicology Program technical report series Pub Date : 2005-01-01
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The numbers of labeled cells and the labeling indices in the left kidney of 200 and 400 ppm F344/N male rats were significantly greater than those in the chamber controls. The alpha2u-globulin/soluble protein ratios were significantly increased in all exposed groups of F344/N rats. Liver weights of male F344/N and NBR rats exposed to 100 ppm or greater were significantly increased, as were those of all exposed groups of females. Kidney weights of male F344/N rats exposed to 50 ppm or greater were significantly increased. Exposure-related hyaline droplet accumulation, degeneration and regeneration of renal cortical tubules, and granular casts occurred in the kidney of exposed F344/N male rats. 2-WEEK STUDIES IN MICE: Groups of five male and five female B6C3F(1) mice were exposed to 0, 25, 50, 100, 200, or 400 ppm decalin vapor 6 hours per day, 5 days per week for 17 days. All mice survived to the end of the study, and mean body weights of exposed groups were similar to those of the chamber control groups. Liver weights of 200 and 400 ppm males and females and 100 ppm females were significantly increased. 3-MONTH STUDY IN RATS: Groups of 25 male and 20 female F344/N rats were exposed to 0, 25, 50, 100, 200, or 400 ppm decalin vapor 6 hours per day, 5 days per week for 2 (five male renal toxicity rats), 6 (10 male and 10 female clinical pathology rats), or 14 (10 core study rats) weeks. All rats survived to the end of the study, and mean body weights of exposed groups were similar to those of the chamber control groups. Urinalysis results indicated that decalin exposure caused increases in urine glucose and protein concentrations and enzyme activities that were consistent with the renal lesions observed microscopically. Renal toxicity studies were performed on rats sacrificed at 2 and 6 weeks and at the end of the study. In kidney tissue examined for cell proliferation, the numbers of PCNA-labeled cells and labeling indices were generally significantly greater than those of the chamber controls in exposed groups of rats at all three time points. Concentrations of alpha2u-globulin in the kidney as well as the alpha2u-globulin/soluble protein ratios were significantly increased at week 2 in all exposed groups and in the 200 and 400 ppm groups at week 6 and at the end of the study. Absolute and/or relative kidney and liver weights of male rats exposed to 50 ppm or greater were increased. Incidences of renal tubule regeneration and granular casts in the medulla of the kidney in exposed male rats were increased, and the severities of hyaline droplets generally increased with increasing exposure concentration. 3-MONTH STUDY IN MICE: Groups of 10 male and 10 female B6C3F(1) mice were exposed to 0, 25, 50, 100, 200, or 400 ppm decalin vapor 6 hours per day, 5 days per week for 14 weeks. 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引用次数: 0

Abstract

Decalin is used as an industrial solvent for naphthalene, fats, resins, oils, and waxes. It is also used as a substitute for turpentine in lacquers, paints, and varnishes; as a solvent and stabilizer for shoe polishes and floor waxes; and as a constituent of motor fuels and lubricants. Other applications include use as a paint thinner and remover, a patent fuel in stoves, a high-density fuel in submarine-launched cruise missile systems, and in stain removal and cleaning machinery. Decalin was nominated for study by the National Cancer Institute because of its chemical structure, its potential for consumer exposure, and a lack of adequate testing of the chemical. Male and female F344/N rats and B6C3F(1) mice were exposed to decalin (greater than 99% pure) by inhalation for 2 weeks, 3 months, or 2 years. Groups of male NBR rats were exposed to decalin for 2 weeks. Male NBR rats do not produce alpha2u-globulin; the NBR rats were included to study the relationship of alpha2u-globulin and renal lesion induction. Genetic toxicology studies were conducted in Salmonella typhimurium and mouse peripheral blood erythrocytes. 2-WEEK STUDIES IN RATS: Groups of five male and five female F344/N rats and five male NBR rats were exposed to 0, 25, 50, 100, 200, or 400 ppm decalin vapor 6 hours per day, 5 days per week for 16 days. All rats survived to the end of the study, and mean body weights of exposed groups were similar to those of the chamber controls. Renal toxicity studies were performed in male F344/N and NBR rats. The numbers of labeled cells and the labeling indices in the left kidney of 200 and 400 ppm F344/N male rats were significantly greater than those in the chamber controls. The alpha2u-globulin/soluble protein ratios were significantly increased in all exposed groups of F344/N rats. Liver weights of male F344/N and NBR rats exposed to 100 ppm or greater were significantly increased, as were those of all exposed groups of females. Kidney weights of male F344/N rats exposed to 50 ppm or greater were significantly increased. Exposure-related hyaline droplet accumulation, degeneration and regeneration of renal cortical tubules, and granular casts occurred in the kidney of exposed F344/N male rats. 2-WEEK STUDIES IN MICE: Groups of five male and five female B6C3F(1) mice were exposed to 0, 25, 50, 100, 200, or 400 ppm decalin vapor 6 hours per day, 5 days per week for 17 days. All mice survived to the end of the study, and mean body weights of exposed groups were similar to those of the chamber control groups. Liver weights of 200 and 400 ppm males and females and 100 ppm females were significantly increased. 3-MONTH STUDY IN RATS: Groups of 25 male and 20 female F344/N rats were exposed to 0, 25, 50, 100, 200, or 400 ppm decalin vapor 6 hours per day, 5 days per week for 2 (five male renal toxicity rats), 6 (10 male and 10 female clinical pathology rats), or 14 (10 core study rats) weeks. All rats survived to the end of the study, and mean body weights of exposed groups were similar to those of the chamber control groups. Urinalysis results indicated that decalin exposure caused increases in urine glucose and protein concentrations and enzyme activities that were consistent with the renal lesions observed microscopically. Renal toxicity studies were performed on rats sacrificed at 2 and 6 weeks and at the end of the study. In kidney tissue examined for cell proliferation, the numbers of PCNA-labeled cells and labeling indices were generally significantly greater than those of the chamber controls in exposed groups of rats at all three time points. Concentrations of alpha2u-globulin in the kidney as well as the alpha2u-globulin/soluble protein ratios were significantly increased at week 2 in all exposed groups and in the 200 and 400 ppm groups at week 6 and at the end of the study. Absolute and/or relative kidney and liver weights of male rats exposed to 50 ppm or greater were increased. Incidences of renal tubule regeneration and granular casts in the medulla of the kidney in exposed male rats were increased, and the severities of hyaline droplets generally increased with increasing exposure concentration. 3-MONTH STUDY IN MICE: Groups of 10 male and 10 female B6C3F(1) mice were exposed to 0, 25, 50, 100, 200, or 400 ppm decalin vapor 6 hours per day, 5 days per week for 14 weeks. All mice survived to the end of the study, and mean body weights of exposed groups were similar to those of the chamber control groups. Liver weights of 200 and 400 ppm males and females were significantly increased. There was a significant exposure concentration-related decrease in the absolute spermatid head count and a significant decrease in absolute head count of the 400 ppm group compared to the chamber controls. Incidences of centrilobular cytomegaly of the liver were increased in exposed male mice. 2-YEAR STUDY IN RATS: Groups of 50 male and 50 female F344/N rats were exposed to 0, 25, 50 (male rats only), 100, or 400 ppm (female rats only) decalin vapor 6 hours per day, 5 days per week for 105 weeks. A group of 20 male rats was exposed to 400 ppm. Survival of exposed groups was similar to that of the chamber control groups. Mean body weights of 400 ppm males were slightly less than those of the chamber controls during the second year of the study. Incidences of renal tubule adenoma and adenoma or carcinoma (combined) and of benign or malignant pheochromocytoma (combined) of the adrenal medulla in 100 and 400 ppm males were significantly increased. There was a significant association between nephropathy severity and adrenal pheochromocytoma incidence. Nonneoplastic lesions related to decalin exposure occurred in the kidney of male rats. 2-YEAR STUDY IN MICE: Groups of 50 male and 50 female B6C3F(1) mice were exposed to 0, 25, 100, or 400 ppm decalin vapor 6 hours per day, 5 days per week for 105 weeks. Survival of exposed mice was similar to that of the chamber controls. Mean body weights of exposed groups were generally similar to those of the chamber control groups throughout the study. Increased incidences of hepatocellular neoplasms occurred in 25 and 400 ppm female mice, and the incidences of centrilobular hypertrophy, necrosis, syncytial alteration, and erythrophagocytosis of the liver in 400 ppm males were significantly increased. The incidences of uterine stromal polyp and stromal polyp or stromal sarcoma (combined) occurred with positive trends in female mice.

Pharmacokinetic model: The rate of metabolism of decalin was the same for males and females in rats and mice. Also in rats and mice, decalin metabolism was saturated at less than 400 ppm. Increased labeling indices in male rats were likely due to changes related to alpha2u-globulin.

Genetic toxicology: Decalin was not mutagenic in S. typhimurium strains TA97, TA98, TA100, or TA1535, with or without induced hamster or rat liver S9 enzymes. A small but significant increase in the frequency of micronucleated normochromatic erythrocytes was noted in male mice exposed to decalin for 3 months; however, no induction of micronuclei was observed in female mice.

Conclusions: Under the conditions of these studies, there was clear evidence of carcinogenic activity of decalin in male F344/N rats based on increased incidences of renal tubule neoplasms. The increased incidences of benign or malignant pheochromocytoma (combined) of the adrenal medulla in male rats were also considered to be exposure related. There was no evidence of carcinogenic activity of decalin in female F344/N rats exposed to 25, 100, or 400 ppm. There was no evidence of carcinogenic activity of decalin in male B6C3F(1) mice exposed to 25, 100, or 400 ppm. There was equivocal evidence of carcinogenic activity of decalin in female B6C3F(1) mice based on marginally increased incidences of hepatocellular and uterine neoplasms. Exposure of male rats to decalin resulted in nonneoplastic lesions of the kidney characteristic of alpha2u-globulin accumulation. Nonneoplastic lesions of the liver were observed in male mice exposed to decalin.

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十氢化萘(CAS No. 91-17-8)对F344/N大鼠和B6C3F(1)小鼠的NTP毒理学和致癌作用研究,以及十氢化萘对雄性NBR大鼠的毒理学研究(吸入研究)。
十氢化萘用作萘、脂肪、树脂、油和蜡的工业溶剂。它也被用作油漆、油漆和清漆中松节油的替代品;作为鞋油和地板蜡的溶剂和稳定剂;作为汽车燃料和润滑油的组成部分。其他应用包括用作油漆稀释剂和去除剂,炉子中的专利燃料,潜艇发射的巡航导弹系统中的高密度燃料,以及污渍去除和清洁机械。十氢化萘被提名为国家癌症研究所的研究对象,因为它的化学结构,它对消费者的潜在暴露,以及缺乏对这种化学物质的充分测试。雄性和雌性F344/N大鼠和B6C3F(1)小鼠分别吸入十氢化萘(纯度大于99%)2周、3个月或2年。雄性NBR大鼠各组暴露于十氢化萘2周。雄性NBR大鼠不产生α - u-球蛋白;以NBR大鼠为研究对象,研究α - u-球蛋白与肾损害诱导的关系。对鼠伤寒沙门菌和小鼠外周血进行遗传毒理学研究。大鼠2周研究:5只雄性和5只雌性F344/N大鼠和5只雄性NBR大鼠,每天6小时,每周5天,连续16天暴露于0、25、50、100、200或400 ppm的十氢化萘蒸气中。所有大鼠都活到了研究结束,暴露组的平均体重与对照组相似。对雄性F344/N大鼠和NBR大鼠进行肾毒性研究。200和400 ppm F344/N雄性大鼠左肾中标记细胞数量和标记指标均显著高于对照组。F344/N各暴露组大鼠α - u-球蛋白/可溶性蛋白比值均显著升高。暴露于100ppm或更高浓度的F344/N和NBR雄性大鼠肝脏重量显著增加,所有暴露组的雌性大鼠肝脏重量均显著增加。暴露于50ppm或更高浓度的雄性F344/N大鼠肾脏重量显著增加。暴露的F344/N雄性大鼠肾脏出现与暴露相关的肾皮质小管的透明液滴积聚、变性和再生以及颗粒型铸型。小鼠2周研究:每组5只雄性和5只雌性B6C3F(1)小鼠暴露于0、25、50、100、200或400 ppm的十氢化萘蒸气中,每天6小时,每周5天,持续17天。所有小鼠都存活到研究结束,暴露组的平均体重与对照组相似。200、400 ppm雄性和雌性以及100 ppm雌性的肝脏重量显著增加。在大鼠中进行为期3个月的研究:每组25只雄性和20只雌性F344/N大鼠暴露于0、25、50、100、200或400 ppm的十氢化萘蒸气中,每天6小时,每周5天,连续2周(5只雄性肾毒性大鼠)、6周(10只雄性和10只雌性临床病理大鼠)或14周(10只核心研究大鼠)。所有大鼠都存活到研究结束,暴露组的平均体重与对照组相似。尿分析结果表明,十氢化萘暴露引起尿葡萄糖、蛋白质浓度和酶活性的增加,这与显微镜下观察到的肾脏病变一致。在2周和6周以及研究结束时,对大鼠进行肾脏毒性研究。在检查细胞增殖的肾组织中,在所有三个时间点,暴露组大鼠的pcna标记细胞的数量和标记指数普遍显著高于室对照。在第2周,所有暴露组的肾脏中alphau -球蛋白的浓度以及alphau -球蛋白/可溶性蛋白的比率显著增加,在第6周和研究结束时,200和400 ppm组的肾脏中alphau -球蛋白/可溶性蛋白的比率显著增加。暴露于50ppm或更高浓度的雄性大鼠的绝对和/或相对肾脏和肝脏重量增加。暴露雄性大鼠肾小管再生和肾髓质颗粒型铸型的发生率增加,透明液滴的严重程度普遍随暴露浓度的增加而增加。3个月的小鼠研究:每组10只雄性和10只雌性B6C3F(1)小鼠暴露于0、25、50、100、200或400 ppm的十氢化萘蒸气中,每天6小时,每周5天,持续14周。所有小鼠都存活到研究结束,暴露组的平均体重与对照组相似。200和400 ppm的雄性和雌性肝脏重量显著增加。与室内对照相比,400 ppm组的绝对精子数明显减少,与暴露浓度相关的绝对精子数明显减少。暴露的雄性小鼠肝脏小叶中心巨细胞病发生率增高。 为期2年的大鼠研究:每组50只雄性和50只雌性F344/N大鼠暴露于0、25、50(仅限雄性大鼠)、100或400 ppm(仅限雌性大鼠)十氢化萘蒸气中,每天6小时,每周5天,持续105周。一组20只雄性老鼠暴露在400ppm的环境中。暴露组的存活率与对照组相似。在研究的第二年,400ppm雄性的平均体重略低于对照组。100 ppm和400 ppm男性肾小管腺瘤、腺瘤或癌(合并)和肾上腺髓质良性或恶性嗜铬细胞瘤(合并)的发生率显著增加。肾病严重程度与肾上腺嗜铬细胞瘤发病率有显著相关性。与十氢化萘暴露有关的非肿瘤性病变发生在雄性大鼠的肾脏。为期2年的小鼠研究:每组50只雄性和50只雌性B6C3F(1)小鼠,每天6小时,每周5天,暴露于0、25、100或400 ppm的十氢化萘蒸气中,持续105周。暴露在室内的小鼠的存活率与对照组相似。在整个研究过程中,暴露组的平均体重与试验室对照组的体重大致相似。25和400ppm雌性小鼠肝细胞肿瘤发生率增加,400ppm雄性小鼠肝脏小叶中心肥大、坏死、合胞体改变和红细胞吞噬的发生率显著增加。雌性小鼠子宫间质息肉、间质息肉或间质肉瘤(合并)的发生率呈上升趋势。药代动力学模型:十氢化萘在大鼠和小鼠体内的代谢率雌雄一致。同样在大鼠和小鼠中,十氢化萘的代谢在低于400ppm时达到饱和。雄性大鼠标记指数的增加可能是由于与α - u-球蛋白相关的变化。遗传毒理学:加或不加诱导的仓鼠或大鼠肝脏S9酶对鼠伤寒沙门氏菌TA97、TA98、TA100或TA1535株均无致突变性。在暴露于十氢化萘3个月的雄性小鼠中,微核正染红细胞的频率虽小但显著增加;然而,在雌性小鼠中未观察到微核诱导。结论:在本研究条件下,十氢化萘对雄性F344/N大鼠具有明显的致癌活性,主要表现为肾小管肿瘤的发生率增高。雄性大鼠肾上腺髓质良性或恶性嗜铬细胞瘤(合并)发生率的增加也被认为与暴露有关。在暴露于25,100或400ppm的雌性F344/N大鼠中,没有证据表明十氢化萘具有致癌活性。在暴露于25,100或400ppm的雄性B6C3F(1)小鼠中,没有证据表明十氢化萘具有致癌活性。在雌性B6C3F(1)小鼠中,基于肝细胞和子宫肿瘤发生率的轻微增加,有模棱两可的证据表明十氢化萘具有致癌活性。雄性大鼠暴露于十氢化萘导致肾脏非肿瘤性病变,其特征是α - u-球蛋白积聚。在暴露于十氢化萘的雄性小鼠中观察到肝脏的非肿瘤性病变。
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