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应对多氯联苯(PCB)毒性:食油假单胞菌LB400对PCB介导的应激的生理和全基因组反应。

Coping with polychlorinated biphenyl (PCB) toxicity: Physiological and genome-wide responses of Burkholderia xenovorans LB400 to PCB-mediated stress.

作者信息

Parnell J Jacob, Park Joonhong, Denef Vincent, Tsoi Tamara, Hashsham Syed, Quensen John, Tiedje James M

机构信息

Center for Microbial Ecology, Michigan State University, East Lansing, MI 48824, USA.

出版信息

Appl Environ Microbiol. 2006 Oct;72(10):6607-14. doi: 10.1128/AEM.01129-06. Epub 2006 Aug 21.

Abstract

The biodegradation of polychlorinated biphenyls (PCBs) relies on the ability of aerobic microorganisms such as Burkholderia xenovorans sp. LB400 to tolerate two potential modes of toxicity presented by PCB degradation: passive toxicity, as hydrophobic PCBs potentially disrupt membrane and protein function, and degradation-dependent toxicity from intermediates of incomplete degradation. We monitored the physiological characteristics and genome-wide expression patterns of LB400 in response to the presence of Aroclor 1242 (500 ppm) under low expression of the structural biphenyl pathway (succinate and benzoate growth) and under induction by biphenyl. We found no inhibition of growth or change in fatty acid profile due to PCBs under nondegrading conditions. Moreover, we observed no differential gene expression due to PCBs themselves. However, PCBs did have a slight effect on the biosurface area of LB400 cells and caused slight membrane separation. Upon activation of the biphenyl pathway, we found growth inhibition from PCBs beginning after exponential-phase growth suggestive of the accumulation of toxic compounds. Genome-wide expression profiling revealed 47 differentially expressed genes (0.56% of all genes) under these conditions. The biphenyl and catechol pathways were induced as expected, but the quinoprotein methanol metabolic pathway and a putative chloroacetaldehyde dehydrogenase were also highly expressed. As the latter protein is essential to conversion of toxic metabolites in dichloroethane degradation, it may play a similar role in the degradation of chlorinated aliphatic compounds resulting from PCB degradation.

摘要

多氯联苯(PCBs)的生物降解依赖于需氧微生物的能力,例如嗜麦芽窄食单胞菌LB400菌株,其能够耐受PCB降解所呈现的两种潜在毒性模式:被动毒性,因为疏水性PCBs可能破坏膜和蛋白质功能;以及不完全降解中间体产生的降解依赖性毒性。我们监测了LB400在结构联苯途径低表达(琥珀酸盐和苯甲酸盐生长)以及联苯诱导条件下,对Aroclor 1242(500 ppm)存在的生理特征和全基因组表达模式。我们发现在非降解条件下,PCBs不会抑制生长或改变脂肪酸谱。此外,我们观察到PCBs本身不会导致基因表达差异。然而,PCBs确实对LB400细胞的生物表面积有轻微影响,并导致轻微的膜分离。在联苯途径激活后,我们发现PCBs在指数期生长后开始抑制生长,这表明有毒化合物的积累。全基因组表达谱分析显示在这些条件下有47个差异表达基因(占所有基因的0.56%)。如预期的那样,联苯和儿茶酚途径被诱导,但醌蛋白甲醇代谢途径和一个假定的氯乙醛脱氢酶也高度表达。由于后一种蛋白质对于二氯乙烷降解中有毒代谢物的转化至关重要,它可能在PCB降解产生的氯代脂肪族化合物的降解中发挥类似作用。

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