Beland F A
Department of Biochemistry, University of Arkansas for Medical Sciences, Little Rock 72205.
Res Rep Health Eff Inst. 1986 Aug(4):3-30.
Dinitropyrenes are contaminants in diesel emissions that are mutagenic in bacteria and mammalian cells, and tumorigenic in laboratory animals. In this project, we investigated the factors that contributed to the extreme genotoxicity of dinitropyrenes in bacteria and determined if these factors were important in mammalian cells. Xanthine oxidase, a mammalian nitroreductase, catalyzed the conversion of the dinitropyrenes to DNA-bound products, but the level of binding did not exceed that observed with 1-nitropyrene. This suggested that factors in addition to nitroreduction were important in the metabolic activation of dinitropyrenes. 1-Nitro-6-nitrosopyrene and 1-nitro-8-nitrosopyrene were synthesized and reacted with DNA under reducing conditions. The same C8-substituted deoxyguanosine adducts were formed that were found in the xanthine oxidase-catalyzed reactions, which confirmed that incubation with this nitroreductase generated reactive N-hydroxy arylamine intermediates. In incubations with rat and human liver microsomes and cytosol, 1-nitropyrene and 1,3-dinitropyrene were reduced to a lesser extent than 1,6- and 1,8-dinitropyrene, which was in accord with their relative mutagenicities. Each of the cytosolic incubations were similar in that oxygen decreased aminopyrene, but not nitrosopyrene, formation. The data indicated that reduced derivatives of the nitrosopyrenes were redox cycling with oxygen, which decreased cytosolic aminopyrene formation. In cytosolic incubations, oxygen inhibited the reduction of 1-nitropyrene and 1,3-dinitropyrene to a greater extent than 1,6- and 1,8-dinitropyrene. By comparison, in microsomal investigations, the nitroreduction of each nitrated pyrene was equally oxygen-sensitive. This apparently was caused by the initial nitroanion radicals reacting with oxygen to decrease nitrosopyrene formation. Although more extensive nitroreduction of each compound was detected in anaerobic incubations, aerobic reduction of these compounds did occur and may be important during in vivo exposure to nitrated pyrenes. When rat liver cytosol was incubated with the nitrated pyrenes, very low levels of DNA binding were detected. Addition of acetyl coenzyme A (AcCoA) to these incubations increased the binding of the dinitropyrenes 20- to 40-fold, while the binding of 1-nitropyrene was not affected. The extent of AcCoA- dependent binding of the dinitropyrenes reflected the amount of nitroreduction; however, the increase in binding did not occur with dog liver cytosol, which was known to be deficient in N-acetylases. These results indicated that cytosolic nitroreductases catalyzed the formation of N-hydroxy arylamine intermediates, which in the case of dinitropyrenes were converted to reactive N-acetoxy arylamines by cytosolic AcCoA-dependent acetylases.
二硝基芘是柴油排放物中的污染物,在细菌和哺乳动物细胞中具有致突变性,在实验动物中具有致癌性。在本项目中,我们研究了导致二硝基芘在细菌中具有极强遗传毒性的因素,并确定这些因素在哺乳动物细胞中是否重要。黄嘌呤氧化酶是一种哺乳动物硝基还原酶,它催化二硝基芘转化为与DNA结合的产物,但结合水平不超过1-硝基芘所观察到的水平。这表明除硝基还原外的其他因素在二硝基芘的代谢活化中很重要。合成了1-硝基-6-亚硝基芘和1-硝基-8-亚硝基芘,并在还原条件下与DNA反应。形成了与黄嘌呤氧化酶催化反应中发现的相同的C8-取代脱氧鸟苷加合物,这证实了与这种硝基还原酶孵育会产生反应性N-羟基芳胺中间体。在用大鼠和人肝微粒体及胞液进行的孵育中,1-硝基芘和1,3-二硝基芘的还原程度低于1,6-和1,8-二硝基芘,这与其相对致突变性一致。每个胞液孵育的情况相似,即氧气会减少氨基芘的形成,但不会减少亚硝基芘的形成。数据表明,亚硝基芘的还原衍生物与氧气发生氧化还原循环,从而减少了胞液中氨基芘的形成。在胞液孵育中,氧气对1-硝基芘和1,3-二硝基芘还原的抑制作用比对1,6-和1,8-二硝基芘的抑制作用更大。相比之下,在微粒体研究中,每种硝化芘的硝基还原对氧气的敏感性相同。这显然是由于最初的硝基阴离子自由基与氧气反应减少了亚硝基芘的形成。尽管在厌氧孵育中检测到每种化合物的硝基还原更广泛,但这些化合物的需氧还原确实发生了,并且在体内接触硝化芘期间可能很重要。当用硝化芘孵育大鼠肝细胞液时,检测到的DNA结合水平非常低。向这些孵育体系中添加乙酰辅酶A(AcCoA)可使二硝基芘的结合增加20至40倍,而1-硝基芘的结合不受影响。二硝基芘依赖AcCoA的结合程度反映了硝基还原的量;然而,在已知缺乏N-乙酰化酶的狗肝细胞液中,结合并未增加。这些结果表明,胞液硝基还原酶催化形成N-羟基芳胺中间体,就二硝基芘而言,这些中间体被胞液中依赖AcCoA的乙酰化酶转化为反应性N-乙酰氧基芳胺。