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生长基质对表达加氧酶细菌降解三氯生潜力的影响。

Effects of growth substrate on triclosan biodegradation potential of oxygenase-expressing bacteria.

机构信息

Zachry Department of Civil Engineering, Texas A&M University, College Station, TX 77843-3136, USA.

出版信息

Chemosphere. 2013 Nov;93(9):1904-11. doi: 10.1016/j.chemosphere.2013.06.069. Epub 2013 Jul 23.

Abstract

Triclosan is an antimicrobial agent, an endocrine disrupting compound, and an emerging contaminant in the environment. This is the first study investigating triclosan biodegradation potential of four oxygenase-expressing bacteria: Rhodococcus jostii RHA1, Mycobacterium vaccae JOB5, Rhodococcus ruber ENV425, and Burkholderia xenovorans LB400. B. xenovorans LB400 and R. ruber ENV425 were unable to degrade triclosan. Propane-grown M. vaccae JOB5 can completely degrade triclosan (5 mg L(-1)). R. jostii RHA1 grown on biphenyl, propane, and LB medium with dicyclopropylketone (DCPK), an alkane monooxygenase inducer, was able to degrade the added triclosan (5 mg L(-1)) to different extents. Incomplete degradation of triclosan by RHA1 is probably due to triclosan product toxicity. The highest triclosan transformation capacity (Tc, defined as the amount of triclosan degraded/the number of cells inactivated; 5.63×10(-3) ng triclosan/16S rRNA gene copies) was observed for biphenyl-grown RHA1 and the lowest Tc (0.20×10(-3) ng-triclosan/16S rRNA gene copies) was observed for propane-grown RHA1. No triclosan degradation metabolites were detected during triclosan degradation by propane- and LB+DCPK-grown RHA1. When using biphenyl-grown RHA1 for degradation, four chlorinated metabolites (2,4-dichlorophenol, monohydroxy-triclosan, dihydroxy-triclosan, and 2-chlorohydroquinone (a new triclosan metabolite)) were detected. Based on the detected metabolites, a meta-cleavage pathway was proposed for triclosan degradation.

摘要

三氯生是一种抗菌剂、内分泌干扰化合物,也是环境中的一种新兴污染物。本研究首次考察了 4 种表达加氧酶的细菌(红球菌 RHA1、分枝杆菌 JOB5、红球菌 ENV425 和恶臭假单胞菌 LB400)对三氯生的生物降解潜力。恶臭假单胞菌 LB400 和红球菌 ENV425 不能降解三氯生。以丙烷为碳源生长的分枝杆菌 JOB5 能完全降解三氯生(5mg/L)。以联苯、丙烷和添加二环丙基甲酮(DCPK,烷烃单加氧酶诱导剂)的 LB 培养基培养的 R. jostii RHA1 能不同程度地降解添加的三氯生(5mg/L)。RHA1 对三氯生的不完全降解可能是由于三氯生产物的毒性。联苯培养的 RHA1 的三氯生转化能力最高(Tc,定义为降解的三氯生量/失活细胞数;5.63×10(-3)ng 三氯生/16S rRNA 基因拷贝),而丙烷培养的 RHA1 的 Tc 最低(0.20×10(-3)ng 三氯生/16S rRNA 基因拷贝)。在丙烷和 LB+DCPK 培养的 RHA1 降解三氯生过程中,未检测到三氯生降解代谢物。当使用联苯培养的 RHA1 进行降解时,检测到四个氯化代谢物(2,4-二氯苯酚、单羟基三氯生、二羟基三氯生和 2-氯对苯二酚(三氯生的一种新代谢物))。根据检测到的代谢物,提出了三氯生降解的间位裂解途径。

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