Platt Karl L, Degenhardt Christian, Grupe Stefanie, Frank Heinz, Seidel Albrecht
Institute of Toxicology, University of Mainz, Obere Zahlbacher Strasse 67, D-55131 Mainz, Germany.
Chem Res Toxicol. 2002 Mar;15(3):332-42. doi: 10.1021/tx010131t.
Metabolically formed dihydrodiol epoxides in the bay-region of polycyclic aromatic hydrocarbons are thought to be responsible for the genotoxic properties of these environmental pollutants. The hexacyclic aromatic hydrocarbon dibenzo[def,mno]chrysene (anthanthrene), although lacking this structural feature, was found to exhibit considerable bacterial mutagenicity in histidine-dependent strains TA97, TA98, TA100, and TA104 of S. typhimurium in the range of 18-40 his(+)-revertant colonies/nmol after metabolic activation with the hepatic postmitochondrial fraction of Sprague-Dawley rats treated with Aroclor 1254. This mutagenic effect amounted to 44-84% of the values determined with benzo[a]pyrene under the same conditions. The specific mutagenicity of anthanthrene in strain TA100 obtained with the cell fraction of untreated animals was 6 his(+)-revertant colonies/nmol and increased 2.7-fold after treatment with phenobarbital and 4.5-fold after treatment with 3-methylcholanthrene. To elucidate the metabolic pathways leading to genotoxic metabolites, the microsomal biotransformation of anthanthrene was investigated. A combination of chromatographic, spectroscopic, and biochemical methods allowed the identification of the trans-4,5-dihydrodiol, 4,5-oxide, 4,5-, 1,6-, 3,6-, and 6,12-quinones, and 1- and 3-phenols. Furthermore, two diphenols derived from the 3-phenol, possibly the 3,6 and 3,9 positional isomers, as well as two phenol dihydrodiols were isolated. Three pathways of microsomal biotransformation of anthanthrene could be distinguished: The K-region metabolites are formed via pathway I dominated by monooxygenases of the P450 1B subfamily. On pathway II the polynuclear quinones of anthanthrene are formed. Pathway III is preferentially catalyzed by monooxygenases of the P450 1A subfamily and leads to the mono- and diphenols of anthanthrene. The K-region oxide and the 3-phenol are the only metabolites of anthanthrene with strong intrinsic mutagenicity, qualifying them as ultimate mutagens or their precursors. From the intrinsic mutagenicity of these two metabolites and their metabolic formation, the maximal mutagenic effect was calculated. This demonstrates the dominating role of pathway III in the mutagenicity of anthanthrene under conditions where it exhibits the strongest bacterial mutagenicity.
多环芳烃海湾区域代谢形成的二氢二醇环氧化物被认为是这些环境污染物具有遗传毒性的原因。六环芳烃二苯并[def,mno] Chrysene(蒽嵌蒽),虽然缺乏这种结构特征,但发现在经Aroclor 1254处理的Sprague-Dawley大鼠肝线粒体后组分代谢活化后,在鼠伤寒沙门氏菌的组氨酸依赖菌株TA97、TA98、TA100和TA104中表现出相当大的细菌诱变性,范围为18 - 40个his(+)-回复菌落/ nmol。这种诱变效应相当于在相同条件下用苯并[a]芘测定值的44 - 84%。未处理动物细胞组分在TA100菌株中蒽嵌蒽的比诱变性为6个his(+)-回复菌落/ nmol,用苯巴比妥处理后增加2.7倍,用3 -甲基胆蒽处理后增加4.5倍。为了阐明导致遗传毒性代谢物的代谢途径,研究了蒽嵌蒽的微粒体生物转化。结合色谱、光谱和生化方法,鉴定出反式-4,5 -二氢二醇、4,5 -氧化物、4,5 -、1,6 -、3,6 -和6,12 -醌以及1 -和3 -酚。此外,分离出了两种源自3 -酚的二酚,可能是3,6和3,9位置异构体,以及两种酚二氢二醇。蒽嵌蒽微粒体生物转化可分为三条途径:K区域代谢物通过以P450 1B亚家族单加氧酶为主的途径I形成。在途径II上形成蒽嵌蒽的多核醌。途径III优先由P450 1A亚家族的单加氧酶催化,导致蒽嵌蒽的单酚和二酚。K区域氧化物和3 -酚是蒽嵌蒽仅有的具有强内在诱变性的代谢物,使其成为最终诱变剂或其前体。根据这两种代谢物的内在诱变性及其代谢形成,计算出最大诱变效应。这证明了在蒽嵌蒽表现出最强细菌诱变性的条件下,途径III在其诱变性中起主导作用。