Whysner J, Montandon F, McClain R M, Downing J, Verna L K, Steward R E, Williams G M
Toxicology and Risk Assessment Program, American Health Foundation, Valhalla, New York 10595, USA.
Toxicol Appl Pharmacol. 1998 Jan;148(1):14-23. doi: 10.1006/taap.1997.8311.
Phenobarbital (PB), polychlorinated biphenyls (PCBs), and chlordane (CLD) increase liver tumor incidences in rodents, and all are tumor promoters. Most indirect tests for DNA reactivity, including mutagenicity and chromosomal damage, have been negative with these agents. Consequently, the modes of action for tumorigenesis by these compounds are not believed to involve direct DNA reactivity; however, only limited information from direct tests is available for the lack of DNA adduct formation. PB, PCBs, and CLD were tested for DNA adduct formation in the liver of male and female B6C3F1 mice after either single or 2-week dietary exposures. Single gavage dose levels were as follows: PB, 200 mg/kg; PCBs, 50 mg/kg; and CLD, 50 mg/kg. Dietary dose levels were as follows: PB, 1000 ppm; PCBs, 200 ppm and CLD, 200 ppm. Animals were killed 24 h following the end of test-substance administration. DNA was extracted from the liver, and DNA adduct concentrations were enriched using either 1-butanol extraction of adducted nucleotides or nuclease P1 digestion of unadducted nucleotides. Using this protocol, none of the three test compounds produced DNA adducts detected by 32P-postlabeling. Similar negative results were obtained for DNA from the livers of both male and female mice receiving either single or 2-week exposures. The two positive controls, benzidine for the 1-butanol extraction procedure and 2-acetylaminofluorene for the nuclease P1 procedure, showed the expected patterns of DNA adducts. These results support the conclusion that the carcinogenicity of PB, PCBs, and CLD in experimental animals is not the result of direct DNA reactivity, but involves epigenetic mechanisms.
苯巴比妥(PB)、多氯联苯(PCBs)和氯丹(CLD)可增加啮齿动物肝脏肿瘤的发生率,且均为肿瘤促进剂。大多数针对DNA反应性的间接检测,包括致突变性和染色体损伤检测,对这些物质的检测结果均为阴性。因此,人们认为这些化合物的致癌作用方式并不涉及直接的DNA反应性;然而,由于缺乏DNA加合物形成的相关信息,直接检测仅提供了有限的数据。对雄性和雌性B6C3F1小鼠进行单次或为期2周的饮食暴露后,检测PB、PCBs和CLD在其肝脏中是否形成DNA加合物。单次灌胃剂量水平如下:PB为200 mg/kg;PCBs为50 mg/kg;CLD为50 mg/kg。饮食剂量水平如下:PB为1000 ppm;PCBs为200 ppm;CLD为200 ppm。在受试物质给药结束后24小时处死动物。从肝脏中提取DNA,并使用加合核苷酸的1-丁醇提取法或未加合核苷酸的核酸酶P1消化法富集DNA加合物浓度。采用该方案,三种受试化合物均未产生通过32P后标记法检测到的DNA加合物。接受单次或2周暴露的雄性和雌性小鼠肝脏DNA也得到了类似的阴性结果。两种阳性对照,即1-丁醇提取法用的联苯胺和核酸酶P方法用的2-乙酰氨基芴,均显示出预期的DNA加合物模式。这些结果支持了以下结论:PB、PCBs和CLD在实验动物中的致癌性并非直接DNA反应性的结果,而是涉及表观遗传机制。