Bevan D R, Manger W E
Chem Biol Interact. 1985 Dec 17;56(1):13-28. doi: 10.1016/0009-2797(85)90036-5.
Mechanisms of co-carcinogenicity of particulates, such as iron oxide and asbestos, and benzo[a]pyrene (B[a]P) are not completely understood. Particulates dramatically alter rates of uptake of B[a]P into membranes, a factor which could account for co-carcinogenicity. However, B[a]P must be activated to reactive forms to be carcinogenic and mutagenic so alterations in metabolism of B[a]P by particulates also could result in co-carcinogenesis. To elucidate mechanisms of particulate-B[a]P co-carcinogenesis, we have correlated rates of uptake of B[a]P into microsomes with metabolism of B[a]P and with mutagenicity of B[a]P in the Ames test. In general, aryl hydrocarbon hydroxylase (AHH) activity paralleled rates of uptake of B[a]P, though some inhibition of AHH activity by particulates which was not attributable to availability of B[a]P was evident. This inhibition was studied further by assaying separately mixed function oxidase and epoxide hydrase activities in the presence of particulates. Both chrysotile and iron oxide inhibited O-deethylation of 7-ethoxyresorufin and hydration of B[a]P-4,5-oxide. To determine effects of this inhibition on activation of B[a]P to reactive forms, we studied profiles of metabolites of B[a]P and mutagenicity of B[a]P. The only alteration in profiles of B[a]P metabolites produced by particulates was that due to effects on rates of uptake. Similarly, mutagenicity of B[a]P was positively correlated with rates of uptake into microsomes. We conclude that the predominant effects of chrysotile and iron oxide are in altering rates of uptake of particle-adsorbed B[a]P. Changes in uptake rates then result in alterations of B[a]P metabolism and mutagenicity.
颗粒物质(如氧化铁和石棉)与苯并[a]芘(B[a]P)的协同致癌机制尚未完全明确。颗粒物质能显著改变B[a]P进入细胞膜的摄取速率,这可能是协同致癌作用的一个因素。然而,B[a]P必须被激活为活性形式才能具有致癌性和致突变性,因此颗粒物质对B[a]P代谢的改变也可能导致协同致癌作用。为了阐明颗粒物质 - B[a]P协同致癌的机制,我们将B[a]P进入微粒体的摄取速率与B[a]P的代谢以及Ames试验中B[a]P的致突变性进行了关联。一般来说,芳烃羟化酶(AHH)活性与B[a]P的摄取速率平行,不过颗粒物质对AHH活性存在一些抑制作用,且这种抑制并非归因于B[a]P的可利用性。通过在颗粒物质存在的情况下分别测定混合功能氧化酶和环氧化物水解酶的活性,对这种抑制作用进行了进一步研究。温石棉和氧化铁均抑制了7 - 乙氧基试卤灵的O - 脱乙基作用以及B[a]P - 4,5 - 氧化物的水化作用。为了确定这种抑制作用对B[a]P激活为活性形式的影响,我们研究了B[a]P的代谢产物谱和B[a]P的致突变性。颗粒物质所产生的B[a]P代谢产物谱的唯一变化是由于对摄取速率的影响所致。同样,B[a]P的致突变性与进入微粒体的摄取速率呈正相关。我们得出结论,温石棉和氧化铁的主要作用是改变颗粒吸附的B[a]P的摄取速率。摄取速率的变化进而导致B[a]P代谢和致突变性的改变。