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From PCBs to highly toxic metabolites by the biphenyl pathway

机译:通过联苯途径从多氯联苯到高毒性代谢物

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摘要

The degradation of polychlorobiphenyls (PCBs) by diverse bacteria, including Burkholderia sp. LB400, is incomplete with a concomitant accumulation of metabolic intermediates. In this study, the toxicity of diverse (chloro)biphenyls and of their biotransformation into the first two metabolic intermediates of the biphenyl pathway, were determined for the model bacterium Escherichia coli. Recombinant E. coli strains expressing different subsets of bph genes of strain LB400 accumulated metabolic intermediates from (chloro)biphenyls. During biotransformation of these compounds into metabolic intermediates, the viability and metabolic kinetics were determined. The toxicity of biotransformation of (chloro)biphenyls into different metabolic intermediates of (chloro)biphenyls varied. Dihydrodiols and dihydroxybiphenyls are very toxic metabolites for bacteria even after short incubation times, affecting the cell viability much more than (chloro)biphenyls. When bacteria transformed 2-CB into dihydrodiol or dihydroxybiphenyl, a great decrease of intact cells and abundant cell lysis was observed by transmission electronic microscopy. Cell viability of Burkholderia sp. LB400 and of E. coli exposed directly to 2,3-dihydroxybiphenyl decreased also drastically. The toxicity of metabolites generated during oxidation of PCBs may partly explain the recalcitrance to biodegradation of these pollutants. Conversion of less toxic compounds into products with increased toxicity resembles the bioactivation of xenobiotics in higher organisms.
机译:多种细菌,包括伯克霍尔德氏菌(Burkholderia sp。)降解多氯联苯(PCB)。 LB400不完整,伴随有代谢中间体的积累。在这项研究中,确定了模型细菌大肠杆菌的各种(氯)联苯的毒性及其向联苯途径的前两个代谢中间体的生物转化的毒性。表达LB400菌株bph基因不同子集的重组大肠杆菌菌株从(氯)联苯中积累了代谢中间体。在这些化合物生物转化为代谢中间体的过程中,测定了其活力和代谢动力学。 (氯)联苯生物转化为(氯)联苯的不同代谢中间体的毒性各不相同。即使在较短的温育时间后,二氢二醇和二羟基联苯对细菌也是剧毒的代谢产物,对细胞活力的影响远大于(氯)联苯。当细菌将2-CB转化为二氢二醇或二羟基联苯时,通过透射电镜观察到完整细胞的大量减少和丰富的细胞裂解。 Burkholderia sp。的细胞活力。 LB400和直接暴露于2,3-二羟基联苯的大肠杆菌也急剧减少。多氯联苯氧化过程中产生的代谢产物的毒性可能部分解释了这些污染物对生物降解的顽固性。将毒性较低的化合物转化为毒性更高的产品,类似于异物在高等生物中的生物活化。

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