Natl Toxicol Program Tech Rep Ser. 2005 Jan(513):1-316.
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.
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.
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.
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.
十氢化萘用作萘、脂肪、树脂、油类及蜡的工业溶剂。它还用作漆、涂料及清漆中松节油的替代品;用作鞋油和地板蜡的溶剂及稳定剂;用作发动机燃料和润滑剂的成分。其他用途包括用作油漆稀释剂和去除剂、炉灶中的专利燃料、潜艇发射巡航导弹系统中的高密度燃料,以及用于污渍去除和清洁机械。由于其化学结构、消费者接触可能性以及对该化学品缺乏充分测试,美国国立癌症研究所将十氢化萘列入研究范围。将雄性和雌性F344/N大鼠及B6C3F(1)小鼠通过吸入方式暴露于纯度大于99%的十氢化萘中,暴露时间为2周、3个月或2年。雄性NBR大鼠组暴露于十氢化萘2周。雄性NBR大鼠不产生α2u球蛋白;纳入NBR大鼠以研究α2u球蛋白与肾损伤诱导之间的关系。在鼠伤寒沙门氏菌和小鼠外周血红细胞中进行了遗传毒理学研究。
大鼠2周研究:将每组5只雄性和5只雌性F344/N大鼠以及5只雄性NBR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,持续16天。所有大鼠均存活至研究结束,暴露组的平均体重与舱内对照组相似。对雄性F344/N和NBR大鼠进行了肾毒性研究。200和400 ppm F344/N雄性大鼠左肾中标记细胞数量和标记指数显著高于舱内对照组。F344/N大鼠所有暴露组的α2u球蛋白/可溶性蛋白比率均显著增加。暴露于100 ppm或更高浓度的雄性F344/N和NBR大鼠以及所有暴露组的雌性大鼠肝脏重量显著增加。暴露于50 ppm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透明滴积累、肾皮质小管变性和再生以及颗粒管型。
小鼠2周研究:将每组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。所有小鼠均存活至研究结束,暴露组的平均体重与舱内对照组相似。200和400 ppm雄性和雌性以及100 ppm雌性小鼠的肝脏重量显著增加。
大鼠3个月研究:将每组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,持续2周(5只雄性肾毒性大鼠)、6周(10只雄性和10只雌性临床病理学大鼠)或14周(10只核心研究大鼠)。所有大鼠均存活至研究结束,暴露组的平均体重与舱内对照组相似。尿液分析结果表明,十氢化萘暴露导致尿葡萄糖和蛋白质浓度以及酶活性增加,这与显微镜下观察到的肾损伤一致。对在2周、6周及研究结束时处死的大鼠进行了肾毒性研究。在检查细胞增殖的肾组织中,所有三个时间点暴露组大鼠的增殖细胞核抗原(PCNA)标记细胞数量和标记指数通常显著高于舱内对照组。所有暴露组在第2周以及200和400 ppm组在第6周及研究结束时,肾脏中α2u球蛋白浓度以及α2u球蛋白/可溶性蛋白比率均显著增加。暴露于50 ppm或更高浓度的雄性大鼠的绝对和/或相对肾脏及肝脏重量增加。暴露雄性大鼠肾脏髓质中肾小管再生和颗粒管型的发生率增加,透明滴的严重程度通常随暴露浓度增加而增加。
小鼠3个月研究:将每组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。所有小鼠均存活至研究结束,暴露组的平均体重与舱内对照组相似。200和400 ppm雄性和雌性小鼠的肝脏重量显著增加。与舱内对照组相比,400 ppm组的绝对精子细胞头数显著减少,且有显著的暴露浓度相关下降。暴露雄性小鼠肝脏小叶中央巨细胞增多症的发生率增加。
大鼠2年研究:将每组50只雄性和50只雌性F344/N大鼠暴露于0、25、50(仅雄性大鼠)、100或400 ppm(仅雌性大鼠)的十氢化萘蒸气中,每天6小时,每周5天,持续105周。一组20只雄性大鼠暴露于400 ppm。暴露组的存活率与舱内对照组相似。在研究的第二年,400 ppm雄性大鼠的平均体重略低于舱内对照组。100和400 ppm雄性大鼠肾小管腺瘤、腺瘤或癌(合并)以及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生率之间存在显著关联。雄性大鼠肾脏出现与十氢化萘暴露相关的非肿瘤性病变。
小鼠2年研究:将每组50只雄性和50只雌性B6C3F(1)小鼠暴露于0、25、100或400 ppm的十氢化萘蒸气中,每天6小时,每周5天,持续105周。暴露小鼠的存活率与舱内对照组相似。在整个研究过程中,暴露组的平均体重通常与舱内对照组相似。25和400 ppm雌性小鼠肝细胞肿瘤的发生率增加,400 ppm雄性小鼠肝脏小叶中央肥大、坏死、合体细胞改变和红细胞吞噬的发生率显著增加。雌性小鼠子宫基质息肉和基质息肉或基质肉瘤(合并)的发生率呈阳性趋势。
大鼠和小鼠中,十氢化萘的代谢速率在雄性和雌性中相同。同样在大鼠和小鼠中,十氢化萘在低于400 ppm时代谢饱和。雄性大鼠标记指数增加可能与α2u球蛋白相关变化有关。
十氢化萘在有或无诱导的仓鼠或大鼠肝脏S9酶的情况下,对鼠伤寒沙门氏菌菌株TA97、TA98、TA100或TA1535均无致突变性。在暴露于十氢化萘3个月的雄性小鼠中,观察到微核正常染色红细胞频率有小但显著的增加;然而,在雌性小鼠中未观察到微核诱导。
在这些研究条件下,基于肾小管肿瘤发生率增加,有明确证据表明十氢化萘对雄性F344/N大鼠具有致癌活性。雄性大鼠肾上腺髓质良性或恶性嗜铬细胞瘤(合并)发生率增加也被认为与暴露有关。在暴露于25、100或400 ppm的雌性F344/N大鼠中,没有十氢化萘致癌活性的证据。在暴露于25、100或400 ppm的雄性B6C3F(1)小鼠中,没有十氢化萘致癌活性的证据。基于肝细胞和子宫肿瘤发生率略有增加,十氢化萘对雌性B6C3F(1)小鼠致癌活性的证据不明确。雄性大鼠暴露于十氢化萘导致肾脏出现以α2u球蛋白积累为特征的非肿瘤性病变。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。