Shin Kwanghee A, Spain Jim C
School of Civil and Environmental Engineering, Georgia Institute of Technology, 311 Ferst Dr., Atlanta, GA 30332-0512, USA.
Appl Environ Microbiol. 2009 May;75(9):2694-704. doi: 10.1128/AEM.02198-08. Epub 2009 Feb 27.
Diphenylamine (DPA) is a common contaminant at munitions-contaminated sites as well as at aniline manufacturing sites. Little is known about the biodegradation of the compound, and bacteria able to use DPA as the growth substrate have not been reported. Burkholderia sp. strain JS667 and Ralstonia sp. strain JS668 were isolated by selective enrichment from DPA-contaminated sediment. The isolates grew aerobically with DPA as the sole carbon, nitrogen, and energy source. During induction of DPA degradation, stoichiometric amounts of aniline accumulated and then disappeared, which suggested that aniline is on the DPA degradation pathway. Genes encoding the enzymes that catalyze the initial steps in DPA degradation were cloned from the genomic DNA of strain JS667. The Escherichia coli clone catalyzed stoichiometric transformation of DPA to aniline and catechol. Transposon mutagenesis, the sequence similarity of putative open reading frames to those of well-characterized dioxygenases, and (18)O(2) experiments support the conclusion that the initial reaction in DPA degradation is catalyzed by a multicomponent ring-hydroxylating dioxygenase. DPA is converted to aniline and catechol via dioxygenation at the 1,2 position of the aromatic ring and spontaneous rearomatization. Aniline and catechol are further biodegraded by the well-established aniline degradation pathway. Genes that encode the complete aniline degradation pathway were found 12 kb downstream of the genes that encode the initial dioxygenase. Expression of the relevant dioxygenases was confirmed by reverse transcription-PCR analysis. Both the sequence similarity and the gene organization suggest that the DPA degradation pathway evolved recently by the recruitment of two gene clusters that encode the DPA dioxygenase and aniline degradation pathway.
二苯胺(DPA)是弹药污染场地以及苯胺制造场地常见的污染物。关于该化合物的生物降解知之甚少,尚未有能利用DPA作为生长底物的细菌的报道。通过从受DPA污染的沉积物中进行选择性富集,分离出了伯克霍尔德氏菌属菌株JS667和罗尔斯通氏菌属菌株JS668。这些分离菌株能以DPA作为唯一的碳源、氮源和能源进行需氧生长。在诱导DPA降解过程中,化学计量的苯胺积累然后消失,这表明苯胺在DPA降解途径上。从菌株JS667的基因组DNA中克隆了编码催化DPA降解初始步骤的酶的基因。大肠杆菌克隆催化DPA化学计量地转化为苯胺和邻苯二酚。转座子诱变、假定的开放阅读框与已充分表征的双加氧酶的序列相似性以及(18)O(2)实验支持了DPA降解的初始反应由多组分环羟基化双加氧酶催化的结论。DPA通过在芳香环的1,2位进行双加氧反应并自发重新芳构化转化为苯胺和邻苯二酚。苯胺和邻苯二酚通过已确立的苯胺降解途径进一步进行生物降解。编码完整苯胺降解途径的基因在编码初始双加氧酶的基因下游12 kb处被发现。通过逆转录 - PCR分析证实了相关双加氧酶的表达。序列相似性和基因组织都表明,DPA降解途径最近通过募集两个编码DPA双加氧酶和苯胺降解途径的基因簇而进化。