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IARC Monogr Eval Carcinog Risks Hum. 2013;101:9-549.
2
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PLoS One. 2013;8(2):e56038. doi: 10.1371/journal.pone.0056038. Epub 2013 Feb 13.
3
Structural characterization of Pandoraea pnomenusa B-356 biphenyl dioxygenase reveals features of potent polychlorinated biphenyl-degrading enzymes.潘多拉菌 B-356 联苯双加氧酶的结构特征揭示了其强效多氯联苯降解酶的特征。
PLoS One. 2013;8(1):e52550. doi: 10.1371/journal.pone.0052550. Epub 2013 Jan 3.
4
Prospects for using combined engineered bacterial enzymes and plant systems to rhizoremediate polychlorinated biphenyls.利用组合工程细菌酶和植物系统进行根际修复多氯联苯的前景。
Environ Microbiol. 2013 Mar;15(3):907-15. doi: 10.1111/1462-2920.12007. Epub 2012 Oct 26.
5
Structural insights into the metabolism of 2-chlorodibenzofuran by an evolved biphenyl dioxygenase.进化的联苯双加氧酶对 2-氯二苯并呋喃代谢的结构见解。
Biochem Biophys Res Commun. 2012 May 18;421(4):757-62. doi: 10.1016/j.bbrc.2012.04.078. Epub 2012 Apr 22.
6
Remarkable ability of Pandoraea pnomenusa B356 biphenyl dioxygenase to metabolize simple flavonoids. 对简单类黄酮具有代谢能力的多形拟盘多毛孢菌 B356 双加氧酶。
Appl Environ Microbiol. 2012 May;78(10):3560-70. doi: 10.1128/AEM.00225-12. Epub 2012 Mar 16.
7
Characterization of biphenyl dioxygenase sequences and activities encoded by the metagenomes of highly polychlorobiphenyl-contaminated soils.高度多氯联苯污染土壤宏基因组中双苯二氧酶序列和活性的表征。
Appl Environ Microbiol. 2012 Apr;78(8):2706-15. doi: 10.1128/AEM.07381-11. Epub 2012 Feb 10.
8
Plant exudates promote PCB degradation by a rhodococcal rhizobacteria.植物渗出物促进了一种土壤杆菌根瘤菌对多氯联苯的降解。
Appl Microbiol Biotechnol. 2012 Sep;95(6):1589-603. doi: 10.1007/s00253-011-3824-z. Epub 2011 Dec 28.
9
Biodegradation of the ultraviolet filter benzophenone-3 under different redox conditions.在不同氧化还原条件下,紫外线过滤剂二苯甲酮-3 的生物降解。
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10
Insight into the metabolism of 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane (DDT) by biphenyl dioxygenases.联苯双加氧酶对 1,1,1-三氯-2,2-双(4-氯苯基)乙烷(滴滴涕)代谢的研究。
Arch Biochem Biophys. 2011 Dec 1;516(1):35-44. doi: 10.1016/j.abb.2011.09.016. Epub 2011 Oct 6.

细菌联苯代谢途径的主要进化目的是降解联苯吗?二苯甲烷案例。

Has the bacterial biphenyl catabolic pathway evolved primarily to degrade biphenyl? The diphenylmethane case.

机构信息

Institut National de Recherche Scientifique, INRS-Institut Armand-Frappier, Laval, Quebec, Canada.

出版信息

J Bacteriol. 2013 Aug;195(16):3563-74. doi: 10.1128/JB.00161-13. Epub 2013 Jun 7.

DOI:10.1128/JB.00161-13
PMID:23749969
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC3754558/
Abstract

In this work, we have compared the ability of Pandoraea pnomenusa B356 and of Burkholderia xenovorans LB400 to metabolize diphenylmethane and benzophenone, two biphenyl analogs in which the phenyl rings are bonded to a single carbon. Both chemicals are of environmental concern. P. pnomenusa B356 grew well on diphenylmethane. On the basis of growth kinetics analyses, diphenylmethane and biphenyl were shown to induce the same catabolic pathway. The profile of metabolites produced during growth of strain B356 on diphenylmethane was the same as the one produced by isolated enzymes of the biphenyl catabolic pathway acting individually or in coupled reactions. The biphenyl dioxygenase oxidizes diphenylmethane to 3-benzylcyclohexa-3,5-diene-1,2-diol very efficiently, and ultimately this metabolite is transformed to phenylacetic acid, which is further metabolized by a lower pathway. Strain B356 was also able to cometabolize benzophenone through its biphenyl pathway, although in this case, this substrate was unable to induce the biphenyl catabolic pathway and the degradation was incomplete, with accumulation of 2-hydroxy-6,7-dioxo-7-phenylheptanoic acid. Unlike strain B356, B. xenovorans LB400 did not grow on diphenylmethane. Its biphenyl pathway enzymes metabolized diphenylmethane, but they poorly metabolize benzophenone. The fact that the biphenyl catabolic pathway of strain B356 metabolized diphenylmethane and benzophenone more efficiently than that of strain LB400 brings us to postulate that in strain B356, this pathway evolved divergently to serve other functions not related to biphenyl degradation.

摘要

在这项工作中,我们比较了 Pandoraea pnomenusa B356 和 Burkholderia xenovorans LB400 代谢联苯甲烷和二苯甲酮的能力,这两种双苯类似物的苯环与单个碳原子相连。这两种化学物质都受到环境的关注。P. pnomenusa B356 能很好地生长在联苯甲烷上。基于生长动力学分析,表明联苯甲烷和二苯甲酮诱导了相同的分解途径。在 B356 菌株以联苯甲烷生长过程中产生的代谢物的图谱与单独作用或偶联反应的二苯并氧杂环戊二烯分解途径的分离酶产生的图谱相同。联苯双加氧酶有效地将联苯甲烷氧化为 3-苄基环己-3,5-二烯-1,2-二醇,最终这种代谢物转化为苯乙酸,苯乙酸进一步通过较低的途径代谢。B356 菌株也能够通过其联苯途径共代谢二苯甲酮,尽管在这种情况下,这种底物不能诱导联苯分解途径,并且降解不完全,积累 2-羟基-6,7-二氧代-7-苯基庚酸。与 B356 菌株不同,B. xenovorans LB400 不能在联苯甲烷上生长。其联苯途径酶代谢联苯甲烷,但代谢二苯甲酮的能力较差。B356 菌株的联苯分解途径比 LB400 菌株更有效地代谢联苯甲烷和二苯甲酮,这使我们假设 B356 菌株的这种途径发生了分歧,以发挥与二苯并氧杂环戊二烯降解无关的其他功能。