首页|1,2-二氯乙烷降解菌群的富集及关键降解菌Ancylobacter sp.BL0的分离鉴定

1,2-二氯乙烷降解菌群的富集及关键降解菌Ancylobacter sp.BL0的分离鉴定

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[目的]1,2-二氯乙烷(1,2-DCA)的污染会危害到人体的生命健康和环境生态安全.为获得高效的 1,2-DCA生物降解种质资源,研究菌群特征并探索从中分离筛选高效 1,2-DCA降解菌株的规律和方法.[方法]从受 1,2-DCA污染的土壤中富集培养能以 1,2-DCA为唯一碳源和能源的降解菌群,通过气相色谱、紫外分光光度仪考察了不同批次菌群的生长和对 1,2-DCA的降解情况,利用高通量测序分析不同批次富集液的物种多样性和相对丰度.通过 16S rDNA基因序列分析鉴定菌株,利用气相色谱-质谱联用测定降解产物,分析菌株的降解途径.[结果]得到了降解菌群BG1,且实验结果显示第 6-11 批和 15 批富集菌群在 24 h内对 12.5 mg/L 1,2-DCA的降解率呈先增加后降低趋势,菌群生物量(OD600)可从 0.03 增长至 0.095,但菌群中Ancylobacter sp.的相对丰度随着持续富集而降低.从第 9 批富集液中筛选出一株菌命名为BL0,鉴定为Ancylobacter sp.,能在 6 h内降解 120 mg/L 1,2-DCA,推测BL0 降解 1,2-DCA的途径为 1,2-DCA水解为 2-氯乙醇,2-氯乙醇再被氧化为氯乙酸,然后被彻底降解利用.[结论]本研究得到了高效降解 1,2-DCA的菌群BG1 和菌株Ancylobacter sp.BL0,同时发现 1,2-DCA降解菌株的筛选分离需要的样品富集过程周期较长且微生物生长量较低,不适于过度富集.菌株Ancylobacter sp.BL0 与富集菌群中的其他菌株之间以竞争关系为主.
Enrichment of 1,2-dichloroethane Degrading Bacterial Consortium,and Isolation and Identification of Ancylobacter sp.BL0 of a Key Degrading Bacterial Strain
[Objective]The pollution of 1,2-dichloroethane(1,2-DCA)will seriously harm human health and environmental ecological safety.In order to obtain efficient 1,2-DCA biodegrading microorganism resources,the characteristics of bacterial flora were studied,and then the rules and methods for separating and screening efficient 1,2-DCA degrading strains were explored.[Method]The bacteria utilizing 1,2-DCA as the sole carbon source and energy were enriched and cultured from soil contaminated by 1,2-DCA.The growth of bacteria and degradation of 1,2-DCA in different batches were investigated by ultraviolet spectrophotometry and gas chromatography respectively.The species diversity and relative abundance of different enriched solution were analyzed by high-throughput sequencing.The strain was identified by 16S rDNA gene sequence analysis.The degraded products were determined by gas chromatography-mass spectrometry,and the degradation pathway was analyzed.[Result]Bacterial consortium BG1 for degradation was gained,and the experimental results showed that the degrading rate of 12.5 mg/L 1,2-DCA by enriched bacterial consortium in batch 6-11 and 15 increased at the beginning and then decreased within 24 h,and the microbial biomass(OD600)increased from 0.03 to 0.095,but the relative abundance of Ancylobacter sp.in the flora decreased with continuous enrichment process.A strain named BL0 was screend from the batch 9 of enrichment solution and identified as Ancylobacter sp.,which degraded 120 mg/L 1,2-DCA within 6 h.It was inferred that the metabolic pathway of degradation of 1,2-DCA by BL0 was hydrolysis of 1,2-DCA to 2-chloroethanol at first,and 2-chloroethanol was oxidized to chloroacetic acid,which was then completely degraded and utilized.[Conclusion]Highly efficient 1,2-DCA degrading bacterial consortium BG1 and strain Ancylobacter sp.BL0 are obtained,and it is found that a long period of sample enrichment is required for screening and separation of 1,2-DCA degrading strains during the process of sample enrichment and low microbial growth is observed,which is not suitable for over-enrichment.Strain Ancylobacter sp.BL0 is competitive with the other strains in the enrichment of bacterial consortium.

1,2-dichloroethanebiodegradationenrichment of bacterial consortiumdegrading consortiumAncylobactercommunity interactionmetabolic pathway

张志梅、张彦猛、谢东明、杨秀云、王浪、左梓涵、吴志国

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天津乐金渤海化学有限公司,天津 300452

天津市丹晟环安科技有限公司,天津 300457

天津科技大学,天津 300457

1,2-二氯乙烷 生物降解 菌群富集 降解菌群 Ancylobacter 群落互作 代谢途径

校企合作技术开发项目

2023120021000787

2024

生物技术通报
中国农业科学院农业信息研究所

生物技术通报

CSTPCD北大核心
影响因子:0.505
ISSN:1002-5464
年,卷(期):2024.40(8)