污染土壤中新分离的三氯乙烯降解菌的系统发育分析

Satoshi Hanada , Toru Shigematsu , Katsutoshi Shibuya , Masahiro Eguchi , Takeshi Hasegawa , Fusako Suda , Yoichi Kamagata , Takahiro Kanagawa , Ryuichiro Kurane
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引用次数: 38

摘要

从三氯乙烯污染天然田中分离到5株甲烷氧化菌(菌株18-2、EB1、KSWIII、KSPIII和KSPIII)和3株芳香族化合物氧化剂(菌株KP22、KP24和KT1)。基于16S rRNA基因序列的系统发育分析表明,所有分离株均属于变形菌纲。菌株18-2和EB1与变形菌门α亚类Methylocystis sp.菌株M亲缘关系密切,序列相似性为98.2% ~ 98.4%,菌株KSWIII、KSPIII和KSPII与变形菌门γ亚类methanica甲基单胞菌相似,序列相似性为97.8 ~ 98.1%。菌株KP22、KP24和KT1归属于变形菌门β亚纲,分别为博德氏菌属(与博德氏菌属的序列相似性为97.2 ~ 97.8%)、洋葱伯克霍尔德氏菌属(序列相似性为99.2%)和富营养Ralstonia(序列相似性为99.4%)。当细胞与适当的底物(即甲烷、苯酚或甲苯)一起生长时,所有分离株都能降解TCE。菌株TCE降解动力学分析表明,菌株TCE降解速率(k1)为10 ~ 36 ml /mg干电池重/h,转化能力(Tc)为0.01 ~ 0.13 mg /mg干电池重。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Phylogenetic analysis of trichloroethylene-degrading bacteria newly isolated from soil polluted with this contaminant

Five methanotrophs (strains 18-2, EB1, KSWIII, KSPIII and KSPIII) and three aromatic compound oxidizers (strains KP22, KP24 and KT1) were isolated from the natural field polluted with trichloroethylene (TCE). Phylogenetic analysis based on 16S rRNA gene sequence suggested that all of the isolates belonged to the class Proteobacteria. Two of the methanotrophic isolates, strains 18-2 and EB1, were closely related to Methylocystis sp. strain M in the α subclass of Proteobacteria with sequence similarities of 98.2–98.4%, while strains KSWIII, KSPIII and KSPII were akin to Methylomonas methanica in the γ subclass of Proteobacteria with sequence similarities of 97.8–98.1%. The aromatic compounds oxidizers, strains KP22, KP24 and KT1, were assigned to the β subclass of Proteobacteria, and classified as Bordetella sp. (97.2–97.8% sequence similarity to species of the genus Bordetella), Burkholderia cepacia (99.2%) and Ralstonia eutropha (99.4%), respectively. All isolates degraded TCE when cells were grown with the appropriate substrate, i.e., methane, phenol or toluene. Detailed kinetic analyses of their TCE degradation revealed that the rates of degradation (k1) among the isolates were 10–36 ml of TCE/mg of dry cell weight/h, and the transformation capacities (Tc) were 0.01–0.13 mg of TCE/mg of dry cell weight.

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