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四氟乙烯(CAS编号:116 - 14 - 3)对F344大鼠和B6C3F1小鼠的NTP毒理学与致癌性研究(吸入研究)

NTP Toxicology and Carcinogenesis Studies of Tetrafluoroethylene (CAS No. 116-14-3) in F344 Rats and B6C3F1 Mice (Inhalation Studies).

出版信息

Natl Toxicol Program Tech Rep Ser. 1997 Apr;450:1-321.

Abstract

Tetrafluoroethylene is used in the production of polytetrafluoroethylene (Teflon(R)) and other polymers. Tetrafluoroethylene was nominated by the National Cancer Institute for toxicity and carcinogenicity studies based on the potential for human exposure to the chemical due to the large production volume and on the lack of adequate data for tetrafluoroethylene in the literature. Male and female F344/N rats and B6C3F1 mice were exposed to tetrafluoroethylene (98% to 99% pure) by whole body inhalation exposure for 16 days, 13 weeks, or 2 years. Genetic toxicity studies were conducted in mouse peripheral blood erythrocytes. 16-DAY STUDY IN RATS: Groups of five male and five female F344/N rats were exposed to 0, 312, 625, 1,250, 2,500, or 5,000 ppm tetrafluoroethylene by inhalation for 6 hours per day, 5 days per week for a total of 12 exposures during a 16-day period. All rats survived to the end of the study. The final mean body weights and body weight gains of males and females exposed to 5,000 ppm were significantly less than those of the controls. The mean body weight gain of females exposed to 2,500 ppm was also significantly less than that of the controls. There were no exposure-related clinical findings in male or female rats. There were no significant differences in hematology parameters that were considered to be related to tetrafluoroethylene exposure. Absolute and relative kidney weights of all exposed groups of males were significantly greater than those of the controls, as were those of females in the 2,500 and 5,000 ppm groups. The absolute kidney weight of females exposed to 1,250 ppm was also significantly greater than that of the controls. The relative liver weights of all exposed groups of males and the absolute liver weights of males in the 625 and 2,500 ppm groups were significantly greater than those of the controls. Increased incidences of renal tubule degeneration occurred in males and females exposed to 625 ppm or greater; this lesion was located predominantly at the corticomedullary junction. The severity of degeneration increased with increasing exposure concentration and was slightly greater in males than females. 16-DAY STUDY IN MICE: Groups of five male and five female B6C3F1 mice were exposed to 0, 312, 625, 1,250, 2,500, or 5,000 ppm tetrafluoroethylene by inhalation for 6 hours per day, 5 days per week for a total of 12 exposures during a 16-day period. All mice survived to the end of the study. Final mean body weights and body weight gains of all exposed groups of mice were similar to those of the controls. There were no exposure-related clinical findings in male or female mice. There were no significant differences in hematology parameters that were considered to be related to tetrafluoroethylene exposure. The absolute and relative liver weights of females exposed to 5,000 ppm were significantly greater than those of the controls, as was the absolute kidney weight of females in that group and the absolute liver weight of females in the 2,500 ppm group. Renal tubule karyomegaly was observed in male and female mice in the 1,250, 2,500, and 5,000 ppm groups, and the severity of this lesion increased with increasing exposure concentration. Karyomegaly was located predominantly in the inner renal cortex. 13-WEEK STUDY IN RATS: Groups of 10 male and 9 or 10 female F344/N rats were exposed to 0, 312, 625, 1,250, 2,500, or 5,000 ppm tetrafluoroethylene by inhalation for 6 hours per day, 5 days per week, for 13 weeks. All rats survived to the end of the study. The final mean body weight and body weight gain of males exposed to 5,000 ppm were significantly less than those of the controls, as was the mean body weight gain of females in this exposure group. There were no clinical findings attributed to exposure to tetrafluoroethylene. Exposure of rats to tetrafluoroethylene resulted in a concentration-dependent normocytic, normochromic, nonresponsive anemia consistent with a secondary hypoproliferative anemia. An exposure concentration-dependent proteinuria also occurred, consistent with renal tubule th renal tubule degeneration observed histopathologically. The absolute and relative liver weights of all exposed groups of males and of females in the 5,000 ppm group were significantly greater than those of the controls. The absolute and relative right kidney weights of males and females exposed to 1,250 ppm or greater and of females in the 625 ppm group were also significantly greater than those of the controls. There were no differences in sperm morphology or vaginal cytology parameters between control and exposed groups of rats. Incidences of renal tubule degeneration in males exposed to 625 ppm or greater and in females exposed to 2,500 or 5,000 ppm were significantly greater than those in the controls. Renal lesions were similar to those observed in the 16-day study and were located predominantly at the corticomedullary junction. 13-WEEK STUDY IN MICE: Groups of 10 male and 10 female B6C3F1 mice were exposed to 0, 312, 625, 1,250, 2,500, or 5,000 ppm tetrafluoroethylene by inhalation for 6 hours per day, 5 days per week, for 13 weeks. All mice survived to the end of the study. Final mean body weights and body weight gains of all exposed groups of male and female mice were generally similar to those of the controls. There were no clinical findings that were considered to be related to tetrafluoroethylene exposure. Exposure of mice to tetrafluoroethylene resulted in a concentration-dependent normocytic, normochromic, nonresponsive anemia, consistent with a secondary hypoproliferative anemia, and in polyuria. Differences in sperm morphology parameters and estrous cycle lengths were not considered to be exposure related. Incidences of karyomegaly of the renal tubule epithelial cells in male and female mice exposed to 1,250 ppm or greater were significantly greater than those in the controls. Karyomegaly was similar to that observed in the 16-day study and was observed primarily in the inner renal cortex. 2-YEAR STUDY IN RATS: Groups of 60 male rats were exposed to 156, 312, or 625 ppm and groups of 60 female rats were exposed to 312, 625, or 1,250 ppm tetrafluoroethylene by inhalation for 6 hours per day, 5 days per week, for 104 weeks, with an observation period of 11 days following the final exposure. Ten male and ten female rats from each exposure group were evaluated at 15 months for organ weights and clinical pathology. Survival, Body Weights, and Clinical Findings: Survival rates of males in the 625 ppm group and of all exposed groups of females were significantly less than those of the controls. Mean body weights of males exposed to 625 ppm were lower than those of the controls from week 81 until the end of the study, and the mean body weight of 1,250 ppm females was slightly lower than that of the controls at the end of the study. The only clinical finding associated with exposure to tetrafluoroethylene was opacity of the eyes in exposed groups of female rats; this change was observed microscopically as cataracts. Hematology, Clinical Chemistry, and Urinalysis: At the 15-month interim evaluation, there were no differences in hematology, clinical chemistry, or urinalysis parameters that were considered to be related to tetrafluoroethylene exposure. Pathology Findings: The absolute and relative kidney weights of males exposed to 625 ppm and females exposed to 1,250 ppm and the absolute kidney weight of females exposed to 625 ppm were significantly greater than those of the controls at the 15-month interim evaluation. At 15 months, renal tubule hyperplasia was observed in one male exposed to 312 ppm and one male and one female exposed to 625 ppm; oncocytic hyperplasia was observed in one female exposed to 1,250 ppm. At the end of the study, incidences of renal tubule adenoma were greater in males and females exposed to 312 ppm or greater than those in the controls. This exposure-related increase was confirmed by examination of step sections (extended evaluations). At the end of the study, the incidences of renal tubule hyperplasia in males exposed to 625 ppm and females exposed to 1,250 ppm were significantly greater than those in the controls. The incidences of renal tubule adenoma and renal tubule adenoma or carcinoma (combined) in the extended evaluations and in the standard and extended evaluations (combined) in the 1,250 ppm female group and the 625 ppm male group were significantly greater than those in the controls, and the incidences occurred with significant positive trends. Oncocytic hyperplasia was observed at the end of the study in one male exposed to 312 ppm and in three females exposed to 1,250 ppm. At 15 months and at the end of the study, the incidences of renal tubule degeneration in all exposed groups of males and in females in the 625 and 1,250 ppm groups were greater than those in the controls. Renal tubule degeneration was similar to that observed in the 13-week study and was located predominantly at the corticomedullary junction. The severity of nephropathy generally increased with increasing exposure concentration in male rats at 15 months and 2 years. The absolute and relative liver weights of females in the 1,250 ppm group and the absolute liver weight of females exposed to 625 ppm were significantly greater than those of the controls at the 15-month interim evaluation. At 2 years, the incidences of hepatocellular carcinoma and hepatocellular adenoma or carcinoma (combined) in males exposed to 312 ppm, the incidences of hepatocellular adenoma and adenoma or carcinoma (combined) in females in all exposed groups, and the incidences of hepatocellular carcinoma in females exposed to 312 or 625 ppm were significantly greater than those in the controls. Also at 2 years, the incidence of hemangiosarcoma in females exposed to 625 ppm was significantly greater than that in the controls. In all exposed groups of males, the incidences of clear cell foci at 15 months were greater than those in the controls; at 2 years, the incidences of eosinophilic foci in all exposed groups of males and the incidences of basophilic and mixed cell foci in males in the 312 and 625 ppm groups were greater than those in the controls. The incidences of mixed cell foci at 15 months in females exposed to 625 or 1,250 ppm and at 2 years in females exposed to 1,250 ppm were also significantly greater than those in the controls. At the end of the 2-year study, increased incidences of cystic degeneration occurred in the liver of all exposed groups of males, and increased incidences of hepatic angiectasis were observed in exposed groups of females. Incidences of mononuclear cell leukemia in males exposed to 156 ppm and in all exposed groups of females were significantly greater than those in the controls. Incidences of cataracts in females exposed to 1,250 ppm were greater than those in the controls at the end of the 2-year study. At the end of the study, there were slight increases in the incidences of testicular interstitial cell adenoma in rats exposed to 312 or 625 ppm. 2-YEAR STUDY IN MICE: Groups of 58 male and 58 female B6C3F1 mice were exposed to 0, 312, 625, or 1,250 ppm tetrafluoroethylene by inhalation for 6 hours per day, 5 days per week, for 95 to 96 weeks. Ten male and ten female mice from each exposure group were evaluated at 15 months for organ weights. Survival, Body Weights, and Clinical Findings: The survival rates of all exposed groups of males and females were significantly less than those of the controls. Because of the reduced survival due to exposure-related liver neoplasms, the study was terminated during week 96. Mean body weights of exposed groups of males and females were generally similar to those of the controls, except at the end of the study, when they were somewhat less than those of the controls. There were no clinical findings related to tetrafluoroethylene exposure. Pathology Findings: At the 15-month interim evaluation, there were no differences in absolute or relative kidney, liver, or lung weights between exposed and control groups of mice. At the end of the study, the incidences of multifocal coagulative necrosis of the liver were increased in males in the 625 and 1,250 ppm groups. Also at the end of the study, females in all exposed groups had greater incidences of hematopoietic cell proliferation in the liver than the controls. Angiectasis occurred in all exposed groups of males and females at 15 months and at the end of the study. At the 15-month interim evaluation, hemangiosarcomas were observed in three males exposed to 1,250 ppm and in one female exposed to 312 ppm. The incidences of hemangiosarcoma in all exposed groups of males and females at the end of the study were significantly greater than those in the controls and exceeded the historical chamber control ranges. Also at the end of the study, the incidences of hemangioma in males and females exposed to 312 ppm and in males exposed to 625 ppm were also significantly greater than those in the controls and exceeded the range in historical chamber controls. At 15 months, hepatocellular adenomas and carcinomas occurred in control males and all exposed groups of males and females. Females exposed to 625 or 1,250 ppm had significantly greater incidences of eosinophilic foci than the controls at the 15-month interim evaluation. At the end of the study, the incidences of eosinophilic foci in males exposed to 625 or 1,250 ppm and in females exposed to 312 or 625 ppm were significantly greater than those in the controls. In male and female mice, increased incidences of a variety of hepatocellular neoplasms, including adenomas, multiple adenomas, carcinomas, and multiple carcinomas, were considered related to tetrafluoroethylene exposure. At the end of the study, the incidences of histiocytic sarcoma (all organs) in all exposed groups of males and females were significantly greater than those in the controls and exceeded the historical control ranges for all organs. The greatest incidences of histiocytic sarcomas were observed in the liver and lung, but these neoplasms were also observed in the spleen, lymph nodes, bone marrow, and kidney. Significantly increased incidences of renal tubule dilatation (males) and karyomegaly (males and females), located predominantly in the inner cortex, were observed in mice exposed to 625 or 1,250 ppm at 15 months. At the end of the study, the increased incidences of dilatation and karyomegaly in all exposed groups of males and of karyomegaly in 1,250 ppm females were generally significant. Incidences of hematopoietic cell proliferation in the spleen of all exposed groups of males and females were significantly greater than those in the controls at the end of the study. Additionally, the severity of this lesion increased with increasing exposure concentration. GENETIC TOXICOLOGY: No increases in the frequency of micronucleated erythrocytes were observed in peripheral blood samples obtained from male and female mice at the end of the 13-week inhalation study of tetrafluoroethylene. CONCLUSIONS: Under the conditions of these 2-year inhalation studies, there was clear evidence of carcinogenic activity of tetrafluoroethylene in male F344/N rats based on increased incidences of renal tubule neoplasms (mainly adenomas) and hepatocellular neoplasms. There was clear evidence of carcinogenic activity of tetrafluoroethylene in female F344/N rats based on increased incidences of renal tubule neoplasms, liver hemangiosarcomas, hepatocellular neoplasms, and mononuclear cell leukemia. There was clear evidence of carcinogenic activity of tetrafluoroethylene in male and female B6C3F1 mice based on increased incidences of liver hemangiomas and hemangiosarcomas, hepatocellular neoplasms, and histiocytic sarcomas. Slight increases in the incidences of mononuclear cell leukemia and testicular interstitial cell adenomas in male rats may have been related to exposure to tetrafluoroethylene. Exposure of rats to tetrafluoroethylene resulted in increased incidences of renal tubule hyperplasia and degeneration in males and females, increased severity of kidney nephropathy in males, and increased incidences of liver angiectasis and cataracts in females. Exposure of mice to tetrafluoroethylene resulted in increased incidences of hematopoietic cell proliferation of the liver in females, liver angiectasis in males and females, renal tubule dilatation in males, renal tubule karyomegaly in males and females, and splenic hematopoietic cell proliferation in males and females. Synonyms: Perfluoroethylene; tetrafluoroethene; 1,1,2,2-tetrafluoroethylene; TFE

摘要

四氟乙烯用于生产聚四氟乙烯(特氟龙®)和其他聚合物。由于四氟乙烯产量大,且文献中缺乏关于它的充分数据,美国国立癌症研究所提名对其进行毒性和致癌性研究。通过全身吸入暴露,让雄性和雌性F344/N大鼠以及B6C3F1小鼠接触纯度为98%至99%的四氟乙烯,暴露时间分别为16天、13周或2年。对小鼠外周血红细胞进行了遗传毒性研究。

大鼠16天研究:将每组5只雄性和5只雌性F344/N大鼠,通过吸入方式,每天暴露6小时,每周5天,在16天内共暴露12次,使其接触浓度为0、312、625、1250、2500或5000 ppm的四氟乙烯。所有大鼠均存活至研究结束。接触5000 ppm的雄性和雌性大鼠的最终平均体重和体重增加量显著低于对照组。接触2500 ppm的雌性大鼠的平均体重增加量也显著低于对照组。雄性和雌性大鼠均未出现与暴露相关的临床症状。在被认为与四氟乙烯暴露相关的血液学参数方面,没有显著差异。所有暴露组雄性大鼠的绝对和相对肾脏重量均显著大于对照组,2500和5000 ppm组的雌性大鼠也是如此。接触1250 ppm的雌性大鼠的绝对肾脏重量也显著大于对照组。所有暴露组雄性大鼠的相对肝脏重量以及625和2500 ppm组雄性大鼠的绝对肝脏重量均显著大于对照组。接触625 ppm及以上的雄性和雌性大鼠肾小管变性的发生率增加;该病变主要位于皮质髓质交界处。变性的严重程度随暴露浓度增加而增加,雄性大鼠的变性程度略高于雌性大鼠。

小鼠16天研究:将每组5只雄性和5只雌性B6C3F1小鼠,通过吸入方式,每天暴露6小时,每周5天,在16天内共暴露12次,使其接触浓度为0、312、625、1250、2500或5000 ppm的四氟乙烯。所有小鼠均存活至研究结束。所有暴露组小鼠的最终平均体重和体重增加量与对照组相似。雄性和雌性小鼠均未出现与暴露相关的临床症状。在被认为与四氟乙烯暴露相关的血液学参数方面,没有显著差异。接触5000 ppm的雌性大鼠的绝对和相对肝脏重量均显著大于对照组,该组雌性大鼠的绝对肾脏重量以及2500 ppm组雌性大鼠的绝对肝脏重量也是如此。在1250、2500和5000 ppm组的雄性和雌性小鼠中观察到肾小管核肿大,且该病变的严重程度随暴露浓度增加而增加。核肿大主要位于肾内皮质。

大鼠13周研究:将每组10只雄性和9或10只雌性F344/N大鼠,通过吸入方式,每天暴露6小时,每周5天,持续13周,使其接触浓度为0、312、625、1250、2500或5000 ppm的四氟乙烯。所有大鼠均存活至研究结束。接触5000 ppm的雄性大鼠的最终平均体重和体重增加量显著低于对照组,该暴露组雌性大鼠的平均体重增加量也是如此。没有归因于四氟乙烯暴露的临床症状。大鼠接触四氟乙烯导致浓度依赖性的正细胞、正色素性、无反应性贫血,符合继发性低增生性贫血。还出现了浓度依赖性蛋白尿,这与组织病理学观察到的肾小管变性一致。所有暴露组雄性大鼠以及5000 ppm组雌性大鼠的绝对和相对肝脏重量均显著大于对照组。接触1250 ppm及以上的雄性和雌性大鼠以及625 ppm组雌性大鼠的绝对和相对右肾重量也显著大于对照组。对照组和暴露组大鼠的精子形态或阴道细胞学参数没有差异。接触625 ppm及以上的雄性大鼠和接触2500或5000 ppm的雌性大鼠的肾小管变性发生率显著高于对照组。肾脏病变与16天研究中观察到的相似,主要位于皮质髓质交界处。

小鼠13周研究:将每组10只雄性和10只雌性B6C3F1小鼠,通过吸入方式,每天暴露6小时,每周5天,持续13周,使其接触浓度为0、312、625、1250、2500或5000 ppm的四氟乙烯。所有小鼠均存活至研究结束。所有暴露组雄性和雌性小鼠的最终平均体重和体重增加量通常与对照组相似。没有被认为与四氟乙烯暴露相关的临床症状。小鼠接触四氟乙烯导致浓度依赖性的正细胞、正色素性、无反应性贫血,符合继发性低增生性贫血,并出现多尿。精子形态参数和发情周期长度的差异不被认为与暴露有关。接触1250 ppm及以上的雄性和雌性小鼠的肾小管上皮细胞核肿大发生率显著高于对照组。核肿大与16天研究中观察到的相似,主要在肾内皮质观察到。

大鼠2年研究:将每组60只雄性大鼠暴露于浓度为156、312或625 ppm的四氟乙烯,每组60只雌性大鼠暴露于浓度为312、625或1250 ppm的四氟乙烯,通过吸入方式,每天暴露6小时,每周5天,持续104周,最后一次暴露后观察1天。在15个月时,对每个暴露组的10只雄性和10只雌性大鼠进行器官重量和临床病理学评估。

存活、体重和临床症状:625 ppm组雄性大鼠以及所有暴露组雌性大鼠的存活率显著低于对照组。从第81周直到研究结束,接触625 ppm的雄性大鼠的平均体重低于对照组,在研究结束时,接触1250 ppm的雌性大鼠的平均体重略低于对照组。与四氟乙烯暴露相关的唯一临床症状是暴露组雌性大鼠出现眼部浑浊;显微镜下观察到这种变化为白内障。

血液学、临床化学和尿液分析:在15个月的中期评估中,在被认为与四氟乙烯暴露相关的血液学、临床化学或尿液分析参数方面没有差异。

病理学发现

在15个月的中期评估中,接触625 ppm的雄性大鼠以及接触1250 ppm的雌性大鼠的绝对和相对肾脏重量,以及接触625 ppm的雌性大鼠的绝对肾脏重量均显著大于对照组。在15个月时,在1只接触312 ppm的雄性大鼠、1只接触625 ppm的雄性大鼠和1只接触625 ppm的雌性大鼠中观察到肾小管增生;在1只接触1250 ppm的雌性大鼠中观察到嗜酸性细胞增生。在研究结束时,接触312 ppm及以上的雄性和雌性大鼠的肾小管腺瘤发生率高于对照组。通过连续切片检查(扩展评估)证实了这种与暴露相关的增加。在研究结束时,接触625 ppm的雄性大鼠和接触1250 ppm的雌性大鼠的肾小管增生发生率显著高于对照组。在扩展评估以及标准和扩展评估(合并)中,1250 ppm雌性组和625 ppm雄性组的肾小管腺瘤和肾小管腺瘤或癌(合并)发生率显著高于对照组,且发生率呈显著正趋势。在研究结束时,在1只接触312 ppm的雄性大鼠和3只接触1250 ppm的雌性大鼠中观察到嗜酸性细胞增生。在15个月和研究结束时,所有暴露组雄性大鼠以及625和1250 ppm组雌性大鼠的肾小管变性发生率均高于对照组。肾小管变性与13周研究中观察到的相似,主要位于皮质髓质交界处。在15个月和2年时,雄性大鼠的肾病严重程度通常随暴露浓度增加而增加。在15个月的中期评估中,1250 ppm组雌性大鼠的绝对和相对肝脏重量以及接触625 ppm的雌性大鼠的绝对肝脏重量均显著大于对照组。在2年时,接触312 ppm的雄性大鼠的肝细胞癌和肝细胞腺瘤或癌(合并)发生率、所有暴露组雌性大鼠的肝细胞腺瘤和腺瘤或癌(合并)发生率以及接触312或625 ppm的雌性大鼠的肝细胞癌发生率均显著高于对照组。同样在2年时,接触625 ppm的雌性大鼠的血管肉瘤发生率显著高于对照组。在所有暴露组雄性大鼠中,15个月时透明细胞灶的发生率高于对照组;在2年时,所有暴露组雄性大鼠的嗜酸性灶发生率以及312和625 ppm组雄性大鼠的嗜碱性和混合细胞灶发生率均高于对照组。在15个月时,接触625或1250 ppm的雌性大鼠的混合细胞灶发生率以及在2年时接触1250 ppm 的雌性大鼠的混合细胞灶发生率也显著高于对照组。在2年研究结束时,所有暴露组雄性大鼠的肝脏出现囊性变性的发生率增加,暴露组雌性大鼠出现肝血管扩张的发生率增加。接触156 ppm的雄性大鼠和所有暴露组雌性大鼠的单核细胞白血病发生率显著高于对照组。在2年研究结束时,接触1250 ppm的雌性大鼠的白内障发生率高于对照组。在研究结束时,接触312或625 ppm的大鼠的睾丸间质细胞腺瘤发生率略有增加。

小鼠2年研究:将每组58只雄性和58只雌性B6C3F1小鼠,通过吸入方式,每天暴露6小时,每周5天,持续95至96周,使其接触浓度为0、312、625或1250 ppm的四氟乙烯。在15个月时,对每个暴露组的10只雄性和10只雌性小鼠进行器官重量评估。

存活、体重和临床症状:所有暴露组雄性和雌性小鼠的存活率显著低于对照组。由于与暴露相关的肝脏肿瘤导致存活率降低,该研究在第96周终止。暴露组雄性和雌性小鼠的平均体重通常与对照组相似,但在研究结束时,它们略低于对照组。没有与四氟乙烯暴露相关的临床症状。

病理学发现

在15个月的中期评估中,暴露组和对照组小鼠的绝对或相对肾脏、肝脏或肺重量没有差异。在研究结束时,625和1250 ppm组雄性小鼠的肝脏多灶性凝固性坏死发生率增加。同样在研究结束时,所有暴露组雌性小鼠肝脏中的造血细胞增殖发生率高于对照组。在15个月和研究结束时,所有暴露组雄性和雌性小鼠均出现血管扩张。在15个月的中期评估中,在3只接触1250 ppm的雄性小鼠和1只接触312 ppm的雌性小鼠中观察到血管肉瘤。在研究结束时,所有暴露组雄性和雌性小鼠的血管肉瘤发生率显著高于对照组,且超过了历史对照组范围。同样在研究结束时,接触312 ppm的雄性和雌性小鼠以及接触625 ppm的雄性小鼠的血管瘤发生率也显著高于对照组,且超过了历史对照组范围。在15个月时,对照组雄性小鼠以及所有暴露组雄性和雌性小鼠均出现肝细胞腺瘤和癌。在15个月的中期评估中,接触625或1250 ppm的雌性小鼠的嗜酸性灶发生率显著高于对照组。在研究结束时,接触625或1250 ppm的雄性小鼠以及接触312或625 ppm的雌性小鼠的嗜酸性灶发生率显著高于对照组。在雄性和雌性小鼠中,多种肝细胞肿瘤(包括腺瘤、多个腺瘤、癌和多个癌)的发生率增加被认为与四氟乙烯暴露有关。在研究结束时,所有暴露组雄性和雌性小鼠的组织细胞肉瘤(所有器官)发生率显著高于对照组,且超过了所有器官的历史对照范围。组织细胞肉瘤发生率最高的是肝脏和肺,但在脾脏、淋巴结、骨髓和肾脏中也观察到这些肿瘤。在15个月时,接触625或1250 ppm的小鼠出现肾小管扩张(雄性)和核肿大(雄性和雌性)的发生率显著增加,主要位于内皮质。在研究结束时,所有暴露组雄性小鼠的扩张和核肿大发生率增加以及1250 ppm雌性小鼠的核肿大发生率增加通常具有显著性。在研究结束时,所有暴露组雄性和雌性小鼠脾脏中的造血细胞增殖发生率显著高于对照组。此外,该病变的严重程度随暴露浓度增加而增加。

遗传毒理学

在四氟乙烯13周吸入研究结束时,从雄性和雌性小鼠外周血样本中未观察到微核红细胞频率增加。

结论

在这些2年吸入研究的条件下,有明确证据表明四氟乙烯对雄性F344/N大鼠具有致癌活性,表现为肾小管肿瘤(主要是腺瘤)和肝细胞肿瘤的发生率增加。有明确证据表明四氟乙烯对雌性F344/N大鼠具有致癌活性,表现为肾小管肿瘤、肝脏血管肉瘤、肝细胞肿瘤和单核细胞白血病的发生率增加。有明确证据表明四氟乙烯对雄性和雌性B6C3F1小鼠具有致癌活性,表现为肝脏血管瘤和血管肉瘤、肝细胞肿瘤和组织细胞肉瘤的发生率增加。雄性大鼠单核细胞白血病和睾丸间质细胞腺瘤发生率的轻微增加可能与四氟乙烯暴露有关。大鼠接触四氟乙烯导致雄性和雌性肾小管增生和变性的发生率增加,雄性肾病严重程度增加,雌性肝脏血管扩张和白内障的发生率增加。小鼠接触四氟乙烯导致雌性肝脏造血细胞增殖的发生率增加,雄性和雌性肝脏血管扩张、雄性肾小管扩张、雄性和雌性肾小管核肿大以及雄性和雌性脾脏造血细胞增殖的发生率增加。

同义词

全氟乙烯;四氟乙烯;1,1,2,2 - 四氟乙烯;TFE

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