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携带 pJP4 的基因生物强化菌对 2,4-D 污染土壤泥浆中土著微生物群落的影响。

Impacts of gene bioaugmentation with pJP4-harboring bacteria of 2,4-D-contaminated soil slurry on the indigenous microbial community.

机构信息

Division of Sustainable Energy and Environmental Engineering, Osaka University, 2-1 Yamadaoka, Suita, Osaka, 565-0871, Japan.

出版信息

Biodegradation. 2012 Apr;23(2):263-76. doi: 10.1007/s10532-011-9505-x. Epub 2011 Aug 18.

DOI:10.1007/s10532-011-9505-x
PMID:21850504
Abstract

Gene bioaugmentation is a bioremediation strategy that enhances biodegradative potential via dissemination of degradative genes from introduced microorganisms to indigenous microorganisms. Bioremediation experiments using 2,4-dichlorophenoxyacetic acid (2,4-D)-contaminated soil slurry and strains of Pseudomonas putida or Escherichia coli harboring a self-transmissible 2,4-D degradative plasmid pJP4 were conducted in microcosms to assess possible effects of gene bioaugmentation on the overall microbial community structure and ecological functions (carbon source utilization and nitrogen transformation potentials). Although exogenous bacteria decreased rapidly, 2,4-D degradation was stimulated in bioaugmented microcosms, possibly because of the occurrence of transconjugants by the transfer of pJP4. Terminal restriction fragment length polymorphism analysis revealed that, although the bacterial community structure was disturbed immediately after introducing exogenous bacteria to the inoculated microcosms, it gradually approached that of the uninoculated microcosms. Biolog assay, nitrate reduction assay, and monitoring of the amoA gene of ammonia-oxidizing bacteria and nirK and nirS genes of denitrifying bacteria showed no irretrievable depressive effects of gene bioaugmentation on the carbon source utilization and nitrogen transformation potentials. These results may suggest that gene bioaugmentation with P. putida and E. coli strains harboring pJP4 is effective for the degradation of 2,4-D in soil without large impacts on the indigenous microbial community.

摘要

基因生物强化是一种生物修复策略,通过从引入的微生物向土著微生物传播降解基因来增强生物降解潜力。在微宇宙中进行了使用 2,4-二氯苯氧乙酸(2,4-D)污染的土壤泥浆和携带可自我传播的 2,4-D 降解质粒 pJP4 的假单胞菌或大肠杆菌菌株的生物修复实验,以评估基因生物强化对整体微生物群落结构和生态功能(碳源利用和氮转化潜力)的可能影响。尽管外源细菌迅速减少,但生物强化微宇宙中的 2,4-D 降解受到了刺激,这可能是因为 pJP4 的转移导致了转导子的出现。末端限制性片段长度多态性分析表明,尽管在将外源细菌引入接种微宇宙后立即扰乱了细菌群落结构,但它逐渐接近未接种微宇宙的结构。Biolog 测定、硝酸盐还原测定以及监测氨氧化细菌的 amoA 基因、反硝化细菌的 nirK 和 nirS 基因表明,基因生物强化对碳源利用和氮转化潜力没有不可挽回的抑制作用。这些结果可能表明,携带 pJP4 的假单胞菌和大肠杆菌菌株的基因生物强化对于土壤中 2,4-D 的降解是有效的,而对土著微生物群落的影响不大。

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