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分析稳定的 1,2-二氯苯降解富集物和两个新分离的降解菌株,食酸菌 sk40 和罗尔斯通氏菌 sk41。

Analysis of stable 1,2-dichlorobenzene-degrading enrichments and two newly isolated degrading strains, Acidovorax sp. sk40 and Ralstonia sp. sk41.

机构信息

Graduate School of Environmental Studies, Tohoku University, Aoba 6-6-20 Aramaki Aoba-ku, Sendai, Miyagi, 980-8579, Japan.

出版信息

Appl Microbiol Biotechnol. 2017 Sep;101(17):6821-6828. doi: 10.1007/s00253-017-8406-2. Epub 2017 Jul 14.

Abstract

Stable degrading 1,2-dichlorobenzene (1,2-DCB) enrichments were generated from original contaminated soil and groundwater via enrichment procedures using a mineral salt medium containing 1,2-DCB as the sole carbon and energy source. Four transferred enrichments showed stable 1,2-DCB-degrading ability and completely degraded 1,2-DCB within 32 h. PCR-denaturing gradient gel electrophoresis (DGGE) and 16S rRNA gene clone library analyses indicated that two bacterial strains, belonging to Acidovorax spp. and Ralstonia spp., respectively, were the predominant organisms in each enrichment. Moreover, these strains maintained a stable coexistence in the four transferred enrichments. These two bacteria were subsequently identified as Acidovorax sp. strain sk40 and Ralstonia sp. strain sk41. Strain sk40 was more tolerant to higher concentrations of 1,2-DCB than strain sk41, while strain sk41 maintained a shorter degradation time under lower concentrations of 1,2-DCB. Notably, however, both strains exhibited similar growth rates and degradation rates in media containing 40 mg/l 1,2-DCB, as well as complete degradation of the 1,2-DCB (40 mg/l) within 32 h. It is expected that these two strains will be used in future applications of bioremediation of 1,2-DCB contamination.

摘要

采用以 1,2-二氯苯(1,2-DCB)为唯一碳源和能源的无机盐培养基,从原始污染土壤和地下水中进行富集培养,得到了具有稳定降解 1,2-DCB 能力的富集物。4 个传代富集物表现出稳定的 1,2-DCB 降解能力,可在 32 h 内完全降解 1,2-DCB。PCR-变性梯度凝胶电泳(DGGE)和 16S rRNA 基因克隆文库分析表明,分别属于 Acidovorax spp. 和 Ralstonia spp. 的两株细菌是每个富集物中的主要微生物。此外,这两株细菌在四个传代富集物中保持稳定的共存关系。这两株细菌随后被鉴定为 Acidovorax sp. strain sk40 和 Ralstonia sp. strain sk41。与 strain sk41 相比,strain sk40 对较高浓度的 1,2-DCB 具有更强的耐受性,而 strain sk41 在较低浓度的 1,2-DCB 下保持更短的降解时间。然而,值得注意的是,这两株细菌在含有 40 mg/l 1,2-DCB 的培养基中表现出相似的生长速度和降解速度,并且可在 32 h 内完全降解 1,2-DCB(40 mg/l)。预计这两株细菌将在未来的 1,2-DCB 污染生物修复应用中得到应用。

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