首页> 外文期刊>International Biodeterioration & Biodegradation >Effects of soil organic matter and bacterial community shift on bioremediation of diesel-contaminated soil.
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Effects of soil organic matter and bacterial community shift on bioremediation of diesel-contaminated soil.

机译:土壤有机质和细菌群落迁移对柴油污染土壤生物修复的影响。

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Bioremediation of diesel-contaminated soils were applied to investigating effects of soil organic matter (SOM) and bacterial community shift. Soil samples were artificially contaminated with diesel oil, ranging from 4000 to 12000 mg/kg soil, remediated with laboratory-scale landfarming batch applications. The SOM levels in our experiment were 2.3% (presented as SOM15), 8.9% (SOM092), and 11.8% (SOM125). Based on each of the SOM levels, bioremediation approaches of bioaugmentation (BA015, BA092, and BA125) and using indigenous microorganisms as control groups (CT015, CT092, and CT125) were tested. After about 300-day operation, total petroleum hydrocarbon (TPH) degradation efficiency became 73%, 63%, and 59% in SOM015, SOM092, and SOM125, respectively. Their 1st order degradation rates also reduced with the increase of SOM. We preliminarily concluded that SOM affected the TPH degradation efficiency and 1st degradation rates. With a logarithm transformation, the degradation pattern of SOM092 and SOM125 found to resemble each other. No apparent improvement was found from the BA batches. Our Intergenic spacer (ITS) microarray result indicated the existence of diesel-degrading bacteria in the indigenous communities. Nonmetric multidimensional scaling (MDS) based on terminal restriction fragment length polymorphism (T-RFLP) data indicated that (1) CT community became similar to BA community, once the 1st degradation stage started, impling an activation of the indigenous bacteria; (2) the degradation stage affected the community dynamics more than the SOM or the remediation approaches could do, and (3) both BA092 and BA125 located in the same cluster on the MDS plot all the time, revealing the similar communities. The similar communities might cause the comparable degradation patterns in SOM092 and SOM125. The bacteria community shift found useful in explaining the TPH degradation performance.
机译:柴油污染土壤的生物修复被用于研究土壤有机质(SOM)和细菌群落迁移的影响。土壤样品被柴油人工污染,范围为4000至12000 mg / kg土壤,并通过实验室规模的土地耕作批量应用进行修复。我们实验中的SOM水平分别为2.3%(表示为SOM15),8.9%(SOM092)和11.8%(SOM125)。根据每个SOM含量,测试了生物强化方法(BA015,BA092和BA125)的生物修复方法,并使用本地微生物作为对照组(CT015,CT092和CT125)。运行约300天后,SOM015,SOM092和SOM125的总石油烃(TPH)降解效率分别为73%,6​​3%和59%。它们的一阶降解率也随着SOM的增加而降低。我们初步得出结论,SOM影响了TPH的降解效率和第一降解率。通过对数转换,发现SOM092和SOM125的降解模式彼此相似。从BA批次中未发现明显改善。我们的基因间隔子(ITS)基因芯片结果表明,土著社区中存在柴油降解细菌。基于末端限制性片段长度多态性(T-RFLP)数据的非度量多维标度(MDS)表明:(1)一旦第一个降解阶段开始,CT群落就与BA群落相似,这意味着本地细菌的活化。 (2)退化阶段对社区动态的影响大于SOM或补救方法所能做到的;(3)位于MDS图上同一集群中的BA092和BA125始终都在显示相似的社区。相似的社区可能会导致SOM092和SOM125中的可比退化模式。发现细菌群落转移可用于解释TPH降解性能。

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